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Enhanced Production of Biofuel from Sugar
Industry Waste
By
Muzna Hashmi
PhD Thesis
Department of Microbiology
Faculty of Biological Sciences
Quaid-i-Azam University
Islamabad, Pakistan
2016
Enhanced Production of Biofuel from Sugar
Industry Waste
A thesis submitted in the partial fulfillment of the requirements for the
degree of
Docter of Philosophy
In
Microbiology
By
Muzna Hashmi
Department of Microbiology
Faculty of Biological Sciences
Quaid-i-Azam University, Islamabad, Pakistan
2016
Enhanced production of biofuel from sugar industry waste Page iii
DECLARATION
The material presented in this thesis is my original work and this work has
never been previously presented for any other degree.
Muzna Hashmi
Enhanced production of biofuel from sugar industry waste Page iv
CERTIFICATE
The Department of Microbiology, Quid-i-Azam University, Islamabad,
accepts this thesis by Muzna Hashmi in its present form as satisfying the
thesis requirement for degree of Doctor of Philosophy in Microbiology.
Supervisor: ________________________
Dr. Aamer Ali Shah
External Examiner: _____________________
_
External Examiner: ______________________
Chairperson: _______________________
Dr. Fariha Hasan
Dated:
Enhanced production of biofuel from sugar industry waste Page v
CONTENTS
Sr. No Titles Page. No.
i. List of Tables iv
ii. List of Figures viii
iii. List of Appendices xi
iv. List of Abbreviation xv
v. Acknowledgment xvi
vi. Abstract xviii
1. Introduction 1
2. Literature Review 9
3. Materials and Methods 40
4. Results 62
5. Discussion 113
6. Conclusions 131
7. Future Prospects 132
8. References 133
8. Appendices 160
Enhanced production of biofuel from sugar industry waste Page vi
List of Tables
No. Tables Page No
4.1. Physicochemical Properties of Molasses 64
4.2.a. Screening of isolated yeast strains against 10%
ethanol tolerance
65
4.2.b. Screening of isolated yeast strains against 15%
ethanol tolerance
66
4.3. Enhanced production of bioethanol by various
yeast strains using different concentration of
sugar
71
4.4. Enhancement of fermentation efficiency due to
optimization
82
4.5. The effect of specific gravity and feeding rate
of molasses on fermentation efficiency and
process completion time of fed batch
fermentation using Lalvin EC-1118
87
4.6. The effect of specific gravity and feeding rate
of molasses on fermentation efficiency and
process completion time of fed batch
fermentation using MZ-4
88
4.7. a. Severity factors for different conditions of
autohydrolysis
91
4.7.b. Severity factors for IL pretreatment conditions 91
4.8.a. Lignin Determination of Autohydrolyzed
Sugarcane bagasse
92
4.8.b. Lignin determination of IL pretreated sugarcane
bagasse
93
4.9.a. Carbohydrate determination of autohydrolyzed
sugarcane bagasse
95
Enhanced production of biofuel from sugar industry waste Page vii
4.9.b. Carbohydrate determination of IL pretreated
sugarcane bagasse
96
4.10. Assignments of FTIR-ATR absorption bands
for bagasse
96
4.11. Crystallinity measurements of autohydrolyzed
and IL pretreated bagasse
101
Enhanced production of biofuel from sugar industry waste Page viii
List of Figures
No Figures Page No.
2.1. Chemical composition of lignocellulosic biomass 23
2.2. Cellulose structure: Crystalline (red); Para-crystalline
(green) and amorphous (blue) chains
25
2.3. Separation of cellulose, hemicelluloses and lignin after
pretreatment of lignocellulosic biomass
35
2.4. Simplistic overview of some factors limiting efficient
hydrolysis of cellulose
37
4.1. Phylogenetic tree of isolated Saccharomyces cerevisiae
strain MZ-4
68
4.2. HPLC chromatogram for ethanol detection 72
4.3. Effect of pH on enhanced production of bioethanol by
Lalvin EC-1118 and MZ-4
74
4.4. Effect of temperature on enhanced production of
bioethanol by Lalvin EC-1118 and MZ-4
74
4.5. Effect of inoculum size on enhanced production of
bioethanol by Lalvin EC-1118 and MZ-4
76
4.6. Effect of inoculum age on enhanced production of
bioethanol by Lalvin EC-1118 and MZ-4
76
4.7. Effect of nitrogen source on enhanced production of
bioethanol by Lalvin EC-1118 and MZ-4
79
4.8. Effect of chelating agents on enhanced production of
bioethanol by Lalvin EC-1118 and MZ-4
81
4.9. The effect of specific gravity and feeding rate for
enhanced production of bioethanol during fed-batch
fermentation using strains Lalvin EC-1118 and MZ-4
86
4.10 Drying and milling of sugarcane bagasse through sieve
size 40 Mesh
90
4.11.a. Sugarcane bagasse autohydrolyzed at 190°C for 10 90
Enhanced production of biofuel from sugar industry waste Page ix
min; 205°C for 6 min and untreated bagasse control
4.11.b. Sugacane bagasse, IL pretreated at 110°C for 30 min;
water treated at 110°C for 30 min (control) and
untreated bagasse (control)
90
4.12. Chromatogram showing peaks of glucose, xylose,
arabinose and mannose standard
94
4.13.a. FTIR spectra of untreated, autohydrolysis and IL
pretreated bagasse from 1800-600 cm-1
region
98
4.13.b. FTIR spectra of untreated, autohydrolysis and IL
pretreated bagasse from 4000 to 1800 cm-1
region
98
4.14. XRD analysis of untreated, autohydrolyzed and IL
pretreated bagasse
100
4.15.a. Enzyme loading optimization for autohydrolyzed
samples
103
4.15.b. Enzyme loading optimization for IL pretreated samples 103
4.16. Chromatogram of sugarcane bagasse hydrolysate
obtained after enzymatic hydrolysis
104
4.17.a. Glucose concentration released from autohydrolyzed
samples during enzymatic hydrolysis
106
4.17.b. Xylose concentration released from autohydrolyzed
samples during enzymatic hydrolysis
106
4.18.a. Cellulose digestibility from autohydrolyzed samples
during enzymatic hydrolysis
107
4.18.b. Xylan digestibility from autohydrolyzed samples
during enzymatic hydrolysis
107
4.19.a Glucose concentration released from IL pretreated
samples during enzymatic hydrolysis
109
4.19.b. Xylose concentration released from IL pretreated
samples during enzymatic
109
4.20.a. Cellulose digestibility from autohydrolyzed samples
during enzymatic hydrolysis
110
Enhanced production of biofuel from sugar industry waste Page x
4.20.b. Xylan digestibility from autohydrolyzed samples during
enzymatic hydrolysis
110
4.21. Production of Bioethanol from untreated, autohydrolyzed
and IL pretreated sugarcane bagasse
112
Enhanced production of biofuel from sugar industry waste Page xi
List of Appendices
No Appendices Page. No.
A Composition of Wallsteiner (WLN) media 161
B Sequence for Strain MZ-4 162
C Standard calibration curves for quantification of sugars and
ethanol
163
C1 Calibration curve for reducing sugar analysis by DNS method 163
C2 Calibration curve for ethanol determination by HPLC method 164
C3 Calibration curve for glucose determination by HPLC method 164
C4 Calibration curve for xylose determination by HPLC method 165
C5 Calibration curve for mannose determination by HPLC method 165
C6 Calibration curve for arabinose determination by HPLC
method
165
D Bioethanol production from sugarcane molasses 166
D.1. Effect of pH on enhanced production of bioethanol by using
Lalvin EC-1118 and MZ-4
167
D.2. Effect of temperature on enhanced production of bioethanol by
using Lalvin EC-1118 and MZ-4
167
D.3. Effect of inoculum size on enhanced production of bioethanol
by using Lalvin EC-1118 and MZ-4
168
D.4. Effect of inoculum age on enhanced production of bioethanol
by using Lalvin EC-1118 and MZ-4
168
D.5. Effect of nitrogen source on enhanced production of
bioethanol by using Lalvin EC-1118 and MZ-4
169
D.6. Effect of chelating agents on enhanced production of
bioethanol by using Lalvin EC-1118 and MZ-4
169
E Ethanol Production from sugarcane bagasse 171
E.1.1. Glucose concentration released from untreated and
autohydrolyzed samples during enzymatic hydrolysis
171
E.1.2. Cellulose digestibility of untreated and autohydrolyzed 171
Enhanced production of biofuel from sugar industry waste Page xii
samples during enzymatic hydrolysis
E.1.3. Xylose concentration released from untreated and
autohydrolyzed samples during enzymatic hydrolysis
172
E.1.4. Xylan digestibility of untreated and autohydrolyzed samples
during enzymatic hydrolysis
172
E.2.1 Glucose concentration released from untreated control, water
treated control and ionic liquid pretreated samples during
enzymatic hydrolysis
173
E.2.2. Cellulose digestibility of untreated control, water treated
control and ionic liquid pretreated samples during enzymatic
hydrolysis
173
E.2.3. Xylose concentration released from untreated control, water
treated control and ionic liquid pretreated samples during
enzymatic hydrolysis
174
E.2.4. Xylan digestibility of untreated control, water treated control
and ionic liquid pretreated samples during enzymatic
hydrolysis
174
E.3.1. Bioethanol production from untreated bagasse by using
various yeast strains
175
E.3.2. Bioethanol production from bagasse autohydrolyzed at 190°C
by using various yeast strains
175
E.3.3. Bioethanol production from bagasse autohydrolyzed at 205°C
by using various yeast strains
175
E.3.4. Bioethanol production from bagasse autohydrolyzed at 110°C
by using various yeast strains
176
E.3.5. Bioethanol production from IL pretreated bagasse at 110°C by
using various yeast strains
176
F. Statistical analysis for the production of bioethanol from
sugarcane molasses
177
F.1. Analysis of variance for the effect of pH on enhanced
production of bioethanol by using Lalvin EC-1118 and MZ-4
177
Enhanced production of biofuel from sugar industry waste Page xiii
F.2. Analysis of variance for the effect of temperature on enhanced
production of bioethanol by using Lalvin EC-1118 and MZ-4
177
F.3. Analysis of variance for the effect of inoculum size on
enhanced production of bioethanol by using Lalvin EC-1118
and MZ-4
178
F.4. Analysis of variance for the effect of inoculum age on
enhanced production of bioethanol by using Lalvin EC-1118
and MZ-4
178
F.5. Analysis of variance for the effect of nitrogen source on
enhanced production of bioethanol by using Lalvin EC-1118
179
F.6. Analysis of variance for the effect of nitrogen source on
enhanced production of bioethanol by using MZ-4
179
F.7. Analysis of variance for the effect of chelating agents on
enhanced production of bioethanol by using Lalvin EC-1118
181
F.8. Analysis of variance for the effect of chelating agents on
enhanced production of bioethanol by using MZ-4
182
F.9. Analysis of variance for the effect of fed batch fermentation on
enhanced production of bioethanol by using Lalvin EC-1118
183
F.10. Analysis of variance for the effect of fed batch fermentation on
enhanced production of bioethanol by using Lalvin EC-1118
183
G. Statistical analysis for the production of bioethanol from
sugarcane bagasse
184
G.1.1. Analysis of variance for the glucose concentration released
from untreated and pretreated bagasse samples during
enzymatic hydrolysis
184
G.1.2. Tukey multiple comparisons for the glucose concentration
released from untreated and pretreated bagasse samples during
enzymatic hydrolysis
185
G.2.1. Analysis of variance for the xylose concentration released
from untreated and pretreated bagasse samples during
enzymatic hydrolysis
186
Enhanced production of biofuel from sugar industry waste Page xiv
G.2.2. Tukey multiple comparisons for the xylose concentration
released from untreated and pretreated bagasse samples during
enzymatic hydrolysis
187
G.3.1. Analysis of variance for the production of bioethanol from
pretreated bagasse by using various yeast strains
188
G.3.2. Tukey multiple comparisons for the production of bioethanol
from pretreated bagasse by using various yeast strains
189
Enhanced production of biofuel from sugar industry waste Page xv
List of Abbreviations
Abbreviation Description
% Percentage
C Celcius
conc. Concentration
CuSO4 Copper sulfate
DNS Dinitrosalycilic acid
DAP Di-ammonium phosphate
DAP Dilute acid pretreatment
EDTA Ethylene diamine-tetraacitic acid
FPU Filter paper assay unit
FTIR Fluorescence transform infrared
spectroscopy
G Gram
h hour
H2SO4 Sulfuric acid
HCl Hydrochloric acid
I Intensity
IL Ionic liquid
K4Fe(CN)6 Potassium ferrocyanide
LAP Laboratory Analytical Protocols
min Minutes
ml milliliter
NA.K. Tartrate Sodium potassium tartarate
NaCl Sodium chloride
NaOH Sodium hydroxide
NCBI National center of biological information
nm Nanometer
NREL National renewable energy lab
OD Optical density
PCR Polymerase chain reaction
RI Refractive index
Rpm rotation per minute
rRNA Ribosome ribonucleic acid
s seconds
Sp. grv. Specific gravity
S.F. Severity factors
Temp. Temperature
WLN Wallerstien
XRD X-Ray Diffraction Crystallography
YPD Yeast extract-peptone-dextrose
β Beta
ul microliter
Enhanced production of biofuel from sugar industry waste Page xvi
Acknowledgement
This thesis is more than just a culmination of a long academic and personal journey, it's a
celebration. This was a long road. But it was also brightly marked with an array of
growing moments that punctuated periods of bleak self-doubt. Only by learning to
humble myself through education, recognizing my weaknesses and limitations, and most
importantly, developing into a person who could effectively seek help from others did I
find the means to push myself and my boundaries. And so, I would like to thank those
who helped me reach the end of this journey, who helped me find strength through their
support, and who guided me onto the brilliant trajectory that I find myself on today.
It gives me great pleasure to express my profound gratitude, sincere thanks and sense of
obligation to my major supervisor, Dr. Aamer ali shah, Associate Professor, Department
of Microbiology, Faculty of biological Sciences, Quaid-i-Azam University (QAU)
Islamabad for his guidance, suggestions, support and encouragement in the completion of
this thesis.
I wish to extend my greatest appreciation to Prof. Dr. Abdul Hameed, Professor,
Department of Microbiology, Faculty of biological Sciences, Quaid-i-Azam University
(QAU) Islamabad for his valuable suggestions and the amazing mentorship and
confidence, who have been integral to the conception, progress and completion of this
research. I am very grateful to Dr. Fariha Hasan, Chairperson Department of
Microbiology for providing all the existing research facilities of the department to
accomplish this work.
I wish to extend my greatest appreciation to Prof. Dr. Safia Ahmed, Prof. Dr. Aftab
Iqbal Shafi and Dr. Malik Badshah, for providing their valuable suggestions, guidance
and encouragement for the completion of this work. . I also want to thank all my teachers
Dr. Rani Faryal, Dr. Naeem Ali, Dr. M. Imran, Dr. Ishtiaq Ali, Dr. Asif Jamal, Dr.
Rubab, Dr. Javaid Dasti and Dr. Samiullah, for their supportive attitude throughout
my research.
I would also like to acknowledge Higher Education Commission of Pakistan and
International Research support Initiative Program (IRSIP) for providing me funds to
complete my research at University of Tennessee, Knoxville, USA, where I worked
under the guidance of Prof. Arthur J. Ragauskas, Professor/Governor’s Chair in
Biorefining, Oak Ridge National Laboratory, Department of Chemical and Biomolecular
Engineering, The University of Tennessee, Knoxville, USA.
Enhanced production of biofuel from sugar industry waste Page xvii
I would like to extend my thanks to Dr. Nicole Labbe’, and Dr. Jingming Tao, Center
of Renewable Carbon, University of Tennessee, Knoxville, USA to provide me analytical
tools and help me for paper write up.
Special thanks go to Director, Murree Brewery for providing me molasses and for all
the beneficial knowledge regarding my research work. I would also like to extend my
thanks to Muhammad Naeem and Ather Hashmi, Technical Experts, Kamstec
International, and Asgher Khan, scientist SB pharma, to provide me HPLC operational
training.
A great depth of loving thanks to my friends Mishal Subhan, Sadia Satti, Leena,
Maria, Sara Shahid, Zimbeel Firdous, Mehreen Zaka, Tehmeena, Sumia Sahar for
their joyous company, lots of love, prayers, encouragement and helping me throughout
my studies. I would like to thank my lab fellows Saima, Aisha siddique, Hira, Afshan
Hina, Maliha Ahmed, Ramla, Anum, Nida Kanwal Nazia, Fozia, Muhammad Rafiq,
Muhammad Irfan, Muttiullah Khatak, Haleem, Waseem, Sahibzada and all others
for their enjoyable company and encouragement during my work.
I would like to thanks my lab fellows Tais, Naijia, Qining, Thomas and Romina
Stoffel for all their cooperation and friendly behavior in University of Tennessee,
Knoxville, USA. A special thank goes to Dr. Tyrone wells for his help, suggestions and
encouragement during my research work and thesis completion.
A non-payable debt to my mother (Masarrat Hashmi), whose love, care and prayers
mean a lot to me. I am also been fortunate to have a great father (Prof. Tufail Hashmi)
who always encouraged me for higher studies and did all his best for my career. Sweet
thanks to my brother Usama, Brother in law (Muhyudin Hashmi), Sister in law (Uzma),
sister (Rashida) and her children (Sidra , Awab, Zuha and Taha) for their love, care,
encouragement, prayers, and patience in bearing me during the tough times of my study.
There are many others around my life who have been helpful to me in many different
ways. There is no way to list all these individuals. I will simply say thank you to my
department, my university and all my fellows around my life that made this work
possible.
God Bless Them ALL.
Muzna Hashmi
Enhanced production of biofuel from sugar industry waste Page xviii
Abstract
The continuous upturn in the cost of petroleum and increasing energy crises has directed
the world’s interest to focus on alternative renewable energy resources. Recently,
bioethanol is emerging as an alternative fuel to substitute gasoline, which is petroleum
derived source of conventional energy. A significant variety of feedstocks can be used for
the production of bioethanol; however, sugar industry waste is considered as the best
option to evade food vs. fuel debate. In this study, two industrial wastes i.e. sugarcane
molasses and bagasse were converted to bioethanol using different microbial strains and
pretreatment strategies. To improve bioethanol production, different yeast strains were
isolated from numerous sources, and MZ-4 labeled strain was selected on the basis of its
maximum ethanol tolerance i.e. 15% (v/v). MZ-4 strain was then identified as
Saccharomyces cerevisiae by 18SrRNA sequencing, and later compared with a
comparatively better commercially available strain Lalvin EC-1118 strain, which was
maximally tolerant to 18% (v/v) ethanol. The physicochemical parameters were
optimized for both strains independently. During batch fermentation by strain MZ-4, the
maximum ethanol yield was determined as 11.1% (v/v) with 69.3% fermentation
efficiency, when pH 5 was adjusted for molasses dilution containing 25% (w/v) sugar
concentration with 10% inoculum before incubation at 33°C for 72 h. However, Lalvin
EC-1118 strain showed comparatively less ethanol yield of 10.9% (v/v) with
fermentation efficiency of 68.1% under its optimal conditions i.e. pH 4.5; inoculum size
of 7.5% and incubation at 30°C for 72 h. Additionally, the study on effect of various
nitrogen sources showed that, MZ-4 produced more ethanol when 0.1% (w/v) NH4Cl was
added; whereas, Lalvin EC-1118 demonstrated better production after the addition of
0.1% (w/v) (NH4)2HPO4. Moreover, it was also observed that MZ-4 and Lalvin EC-1118
exhibited better yields when 0.01 and 0.04% (w/v) of K4Fe(CN)6 was used respectively,
as a chelating agent. During the fed batch fermentation, Lalvin EC-1118 produced a
greater ethanol yield of 13.9% with fermentation efficiency of 81.1%, when 1.090
specific gravity of molasses dilution was adjusted and fed after every 12 h. However, the
strain MZ-4 showed better fermentation efficiency of 83.2% with comparatively less
Enhanced production of biofuel from sugar industry waste Page xix
ethanol yield i.e. 13.5% (v/v) by using molasses dilution of same specific gravity and 24
h feeding interval.
Meanwhile, one of the main challenges for bioethanol production from lignocellulosic
material such as sugarcane bagasse is the recalcitrance of the biomass. A second study
evaluated the efficiency of an ionic liquid (IL) i.e. 1- butyl-3-methyl imidazolium acetate
([C4mim][OAc]) pretreatment at 110°C for 30 min, and compared it with high
temperature autohydrolysis pretreatment (i.e. 110°C for 30 min, 190°C for 10 min and
205°C for 6 min). It was found that sugarcane bagasse exhibited a considerable decrease
in lignin content, reduced cellulose crystallinity, and enhanced cellulose and xylan
digestibility, when subjected to IL pretreatment. Pretreated samples were also
characterized by Fourier transform infrared spectroscopy to verify these findings.
Altogether, cellulose and xylan digestibility of IL pretreated bagasse was determined as
97.4 and 98.6% after 72 h of enzymatic hydrolysis, respectively. In the case of
autohydrolysis, the maximum of cellulose and xylan digestibility was determined after 72
h as 62.1 and 5.7% from bagasse pretreated at 205°C for 6 min, respectively. X-ray
diffraction analysis also showed a significant reduction in crystallinity of IL pretreated
bagasse samples. During fermentation process, IL pretreated and autohydrolyzed bagasse
(205°C for 6 min) exhibited maximum ethanol production of 78.8 and 70.9 mg/g
substrate after 24 h of fermentation, respectively. Comparatively, the fermentation of
bagasse autohydrolyzed at 190°C for 10 min and 110°C for 30 min yielded maximum
ethanol of 66.0 and 28.4 mg/g substrate by using S. cerevisiae Lalvin EC-1118,
respectively. Thus it can be concluded that, fed batch fermentation is employed for the
maximum ethanol yield from sugarcane molasses using Lalvin EC-1118 strain, while IL
pretreated bagasse gives maximum yield when fermented with strain MZ-4.
PhD Thesis
Enhanced production of biofuel from sugar industry waste Page 1
Chapter 1
Introduction
PhD Thesis
Enhanced production of biofuel from sugar industry waste Page 2
Depletion of fossil fuel resources, limited global supply of oil, energy crises and
increasing CO2 emission has increased the worldwide interest to substitute fossil fuels
by some alternative fuel (Huang and Ragauskas, 2012). Today, the ecofriendly biofuel
utilization as a substituent for the petroleum based products, has attracted worldwide
interest for its production at large scale because it can be used in current unmodified
engines by blending it with fossil fuels in different proportions (Macedo, 1998;
Hansen et al., 2005). In order to create more sustainable and economically viable
system, it is more important to emphasize on cheaper ways to produce biofuel to
make it more favorable as compared to petroleum based products (Zabed et al., 2014).
Currently, most popular biofuels being used at different countries are bioethanol,
biodiesel and biogas. The production of biofuel mainly depends on the availability of
substrate and the ease of its formation. Biodiesel are more commonly produced in
Europe from oil containing seeds and plants. However, the production of biogas is
mainly being investigated in Sweden and Germany from the combination of cattle
manure and different agricultural feedstock (Held et al., 2008). In contrast, those
substrates which are rich in sugars are preferably converted in to bioethanol through a
simple process of fermentation (Balat and Balat, 2009). Ethanol can be used in
substituent to gasoline and provide an environmentally safe alternative to fossil fuels
(Macedo, 1998). Currently, ethanol producing industries are utilizing two main types
of feedstock that are sugars and starch containing crops (Wilkie et al., 2000; Mojović
et al., 2006; Balat and Balat, 2009). More than 60% of ethanol among the world is
being produced from sugar crops like sugarcane and rest of 40% is being produced
from starchy grains (Salassi, 2007).
Sugarcane has widely been recognized one of the main biofuel crops in last 10-15
years; because it only requires a simple process of fermentation for the production of
bioethanol from sugarcane juice and molasses (Hartemink, 2008). Sugarcane is
actually a crop of tropical area, which is being cultivated in more than 200 countries,
worldwide. Brazil, ranked second among world’s bioethanol producer, is mainly
utilizing sugarcane juice and molasses for the production of bioethanol. More than
40% of their fuel demands are met from bioethanol (Agama Energy., 2003).
Sugarcane contains 30% more sugars than corn that is widely being used in USA for
the production of bioethanol. Brazil and USA supplies more than 65% of world’s total
ethanol. In Brazil more than 20% of total vehicles have flex fuel engines that are able
PhD Thesis
Enhanced production of biofuel from sugar industry waste Page 3
to consume all proportions of ethanol as fuel. Other vehicles with conventional
engines, can use only ethanol-gasoline blend up to E15 i.e. 15% of ethanol with 85%
of gasoline (Rosillo-Calle and Cortez, 1998).
There are two main types of the wastes generated by sugar industry i.e. molasses and
bagasse. In sugar industry, sugarcane juice is squeezed out under high pressure with
the help of heavy rollers. The juice is clarified, then heated and centrifuged multiple
times to crystallize and separate sugar crystals. Molasses is the non-crystallizable
residues that remain after purification of sucrose from sugarcane juice. This is
moderately economical, rapidly accessible substrate, which is usually utilized as a
feedstock for production of bioethanol. A typical sugar cane molasses normally has
17–25% of water substance, 45–60% of sugar content (sucrose, glucose, and fructose)
and 2–5% of polysaccharides (dextrin, pentose and polyuronic acids). It also contains
the non-sucrose substances, incorporate inorganic salts, kestose, raffinose, natural
acids etc. (Najafpour and Poishan, 2003; da Silva et al., 2012; de Andrade et al.,
2013).
Sugarcane industry is the second largest industry of Pakistan after textile industry.
Pakistan yields 63 million metric tons of sugarcane per anum, and ranks fifth for its
production, worldwide. In Pakistan, there are 83 sugar mills, which annually generate
2.0 million MT molasses that is later converted in to bioethanol (PBS, 2013). High
cost ethanol production from sugarcane molasses can be mainly attributed to low
ethanol content in fermentation media which requires more energy consumption for
distillation process (Zabed et al., 2014). Therefore, efforts are made to enhance
ethanol concentration in fermentation broth to reduce distillation cost (Bai et al.,
2004). Currently Pakistan is producing only 0.13 million MT of ethanol per year
which can be increased to three times, if the fermentation efficiency reaches up to
90%. Fermentation efficiency of the process in most of the distilleries in Pakistan is
less than 50% as estimated by annual sugar report (PBS, 2013). The main hurdle in
increasing the ethanol yield and fermentation efficiency is the selection of most potent
microbial strain for the process of fermentation. Moreover, the final ethanol yield and
fermentation efficiency is also affected by operating the process under unfavorable
physicochemical parameters. Different physicochemical parameters like sugar
concentration, temperature, pH and nutrients are needed to be optimized to determine
PhD Thesis
Enhanced production of biofuel from sugar industry waste Page 4
the best conditions at which maximum yield can be obtained (Wyman and Hinman,
1990).
There are several microorganisms that have the ability to ferment sugars into ethanol.
The most commonly used microorganisms are yeast especially Saccharomyces
cerevisiae (Zhu et al., 2012). S. cerevisiae has the ability to utilize both monomeric
sugars and sucrose, which makes it an efficient microbe to be used in variety of
substrate (Badotti et al., 2008; Canilha et al., 2012). Other advantages related to its
use are its highest resistance against high ethanol concentration, inhibitor resistance
and its ability to consume significant amount of substrate. Unfortunately, S. cerevisiae
lacks genes which could make it able to assimilate xylose; however, to obtain optimal
ethanol yields from sugarcane bagasse, conversion of hemicellulose fraction is also
essential (Canilha et al., 2012). There are only a few species which are capable of
converting xylose ethanol such as Scheffersomyces stipitis (pichia stipites), Candida
guilliermondii, Candida shehatae and Pachysolen tannophilus that can help to
convert xylose, i.e. the second most abundant component of bagasse, into bioethanol
(du Preez et al., 1986; Canilha et al., 2012).
The dried fibrous residue that remains after extraction of juice is termed as bagasse. It
is considered in Brazil that 1 ton of sugarcane will generate 280 kg of bagasse. Total
sugarcane production in 2015 was reported as 1877 million metric tons, worldwide.
Almost 50% of the bagasse is usually burnt in distilleries for power generation and the
remaining is stockpiled. The excess of this industrial waste has raised world’s interest
on biorefinery concept, and now latest researches are being done to convert sugarcane
bagasse into bioethanol (Rabelo et al., 2011).
The major problem face by industry for the production of bioethanol from sugarcane
bagasse is its lignocellulosic structure. Lignocellulosic biomass is a suitable resource
for renewable energy in terms of sustainability and ease of fermentation of
enzymatically released sugars that can be converted into bioethanol to substitute for
gasoline (Li et al., 2010). This resource is mainly composed of cellulose (30–45%),
hemicelluloses (20–30%), and lignin (5–20%) (Vallejos et al., 2012). Cellulose chains
are held together by van der Waals interactions and hydrogen bonding which makes it
a highly crystalline material (Qiu and Aita, 2013). The xylan layer is the most
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prominent hemicelluloses in grasses and hardwoods and forms covalent linkages to
lignin in the cell wall. Xylan also has non-covalent interactions with cellulose, which
are believed to play a role in preventing enzymatic degradation (Ioelovich and Morag,
2012; Qiu and Aita, 2013). Lignin is a complex and branched aromatic structure that
is associated with hemicellulose and contributes to the recalcitrance of biomass (Qiu
and Aita, 2013; Pu et al., 2015). There are several stages involved in conversion of
recalcitrant lignocellulosics into ethanol that include physicochemical pretreatment,
enzymatic hydrolysis, fermentation, ethanol separation and effluent treatment.
Pretreatment is an important step in the overall process and is believed to break down
some of the carbohydrate-lignin complexes (Qiu and Aita, 2013; Yáñez‐S et al.,
2013).
Enzymatic hydrolysis of pretreated biomass is one of the most promising means of
releasing simple sugars from biomass (Batalha et al., 2015). Typically, enzymatic
hydrolysis of un-pretreated biomass is reported to produce less than 20% sugar yield
of theoretical value (Qiu et al., 2012). Different pretreatment methods have been
developed to reduce recalcitrance of lignocellulosic biomass but there are many
drawbacks associated with these procedures. For example biological pretreatments
(i.e. lignin degrading fungi) often require large residence times (Levin et al., 2008;
Dias et al., 2010), mechanical methods such as various grinding and milling
techniques are not appropriate due to their high capital costs and intensive energy
requirements (Naimi et al., 2006). Furthermore, various physicochemical techniques
(e.g. liquid hot water, autohydrolysis, supercritical fluids, steam explosion, dilute
acid, alkali) require high temperature and pressure along with specialized equipment
(Qiu and Aita, 2013; Yu et al., 2013; Batalha et al., 2015). Another drawback
associated with these pretreatments is release of inhibitors, which affect enzymatic
hydrolysis and subsequent fermentation process (Hongdan et al., 2013; Batalha et al.,
2015). These problems highlight the need for a more rapid; environment friendly, cost
effective and efficient method for lignocellulosic biomass conversion.
Despite being energy intensive, autohydrolysis is recommended as environmentally
benign and clean process (Lei et al., 2013) which doesn’t require any catalyst or
corrosive compounds (Hongdan et al., 2013). Biomass and water are heated from
130-230ºC for different time periods (from few seconds to several hours) to carry out
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this pretreatment (Batalha et al., 2015). At high temperature (~200˚C) water has an
acidic pH and acquires catalytic properties which eliminates the requirement of
catalyst to disrupt biomass (Mosier et al., 2005). Auto-ionization of water and
ionization of acidic species (uronic acid and formic acid) at high temperature generate
hydronium ions that catalyze the series of reactions and cause reduction in degree of
polymerization (DP) of hemicelluloses and celluloses by hydrolysis of selective
glycosidic bonds (Lee et al., 2009; Batalha et al., 2015). During autohydrolysis, acetyl
groups are released from substituted xylan chains (along with other organic acids)
which act as catalysts to assist in acid-catalyzed hydrolysis of hemicellulose fraction
of lignocellulosic biomass (Huang and Ragauskas, 2012; Sun et al., 2014; Batalha et
al., 2015; Pol et al., 2015). The main compositional changes observed after
autohydrolysis are lignin transformations and depolymerization of hemicellulose and
celluloses into oligomers and monomers due to very high severity conditions (Batalha
et al., 2015). These compositional changes during autohydrolysis pretreatment create
more number of structural changes including increasing the reducing ends of plant
polysaccharides for efficient exoglucanase activity and hence increased cellulose
digestibility (Huang and Ragauskas, 2012; Hongdan et al., 2013; Batalha et al., 2015).
The significant increase in lignin content after autohydrolysis might be attributed to
the removal of significant amount of hemicellulose while retaining most of the lignin.
The pseudo-lignin can also be generated from carbohydrate without significant
contribution from lignin, especially under high severity pretreatment conditions
(Sannigrahi et al., 2011).
Ionic liquid pretreatment (IL) is another method of reducing the recalcitrance of
biomass that has recently drawn a great deal of attention because of the unique
physical and chemical properties of ILs that are a very stable class of organic salts
with potential application as ―green solvents‖ (Qiu et al., 2012). The main advantages
of using ILs are related to their non-explosive, non-toxic, environment friendly, low
volatility, good recyclability and general stability under severe reaction conditions (Li
et al., 2010; da Silva et al., 2011; Qiu et al., 2012). For biomass pretreatment, three of
the most cited ILs are imidazoliums i.e. [C4mim][Cl] (1-butyl-3-methylimidazolium
chloride), [C2mim][Cl] (1-ethyl-3-methylimidazolium chloride) and [C2mim][OAc]
(1-ethyl-3-methylimidazolium acetate). All these alkylimidazolium salts have been
reported as most effective agents for lignocellulosics dissolution (Karatzos et al.,
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2012). It has been reported that the acetate ion in ILs are less viscous and can function
as a weak base to remove lignin and de-acetylate biomass (Mäki-Arvela et al., 2010;
Karatzos et al., 2012). Studies on these three alkylimidazolium salts reveal that
shorter alkyl chain of [C2mim]+ imparts greater extent of saccharification with faster
dissolution. However, higher dissolution extent of [C2mim]+ does not benefit the
overall process of pretreatment since losses in [C4mim]+-treated biomass were much
less as compared to [C2mim]+ pretreatment process. In terms of hemicellulose
saccharification yield, [C4mim]+ ILs perform better as hemicellulose is preserved in
its polymeric form and recovered form after pretreatment (Karatzos et al., 2012). Due
to these reasons, [C4mim][OAc] (1-butyl-3-methyl imidazolium acetate) pretreatment
was selected for this study. Previously, [C4mim][OAc] pretreatment of sugarcane
bagasse was reported by Silveria et al., (2015), who studied the effect of
[C4mim][OAc] pretreatment in combination with ethanol and supercritical CO2 (at
110, 145 and 180ºC for 2 h); however, Aver et al., (2013) used only [C4mim][OAc]
for the pretreatment at 120ºC for 24 h. Moreover, none of those studies discussed the
effect of [C4mim][OAc] pretreatment on crystallinity of sugarcane bagasse and the
efficiency of fermenting microbes for the production of bioethanol from
[C4mim][OAc] pretreated bagasse. In this study, [C4mim][OAc] was used alone for
pretreatment at comparatively less severe conditions (i.e. 110ºC for 30 min); and
compared with high temperature autohydrolysis to investigate the changes it imparts
to structure and composition of sugarcane bagasse and its potential to produce
bioethanol from sugarcane bagasse. Moreover, the efficiency of various commercially
available yeast strains was compared with a newly isolated strain to determine a better
fermenting strain for enhanced bioethanol production.
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Aim and Objectives
The aim of this study was to enhance the production of bioethanol from the waste
generated by sugar industry i.e. sugarcane molasses and bagasse. This aim of the
study was achieved by formulating following objectives:
Isolation, screening and molecular characterization of indigenous yeast strain
Comparison of indigenous yeast strain with commercially available strain for enhanced
production of bioethanol from sugarcane molasses
Effect of optimized physicochemical parameters on fermentation efficiency and final
ethanol yield from sugarcane molasses
Enhanced production of bioethanol from sugarcane molasses by using fed batch
fermentation
Optimization of feeding rate and substrate concentration during fed batch fermentation
Effect of autohydrolysis and IL pretreatments under different severity conditions on
compositional changes of sugarcane bagasse
Effect of autohydrolysis and IL pretreatments on structural changes of sugarcane bagasse
Effect of autohydrolysis and IL pretreatments on crystallinity of sugarcane bagasse
Effect of autohydrolysis and IL pretreatments on enhanced glucose and xylose release
from sugarcane bagasse during enzymatic hydrolysis
Effect of autohydrolysis and IL pretreatments of sugarcane bagasse on enhanced cellulose
and xylan digestibility during enzymatic hydrolysis
Comparison of indigenous and commercially available yeast strains for enhanced
production of bioethanol from pretreated sugarcane bagass
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Chapter 2
Literature Review
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The world’s energy sector is mainly dependent on non-renewable petroleum products.
In last few decades, an increase in population also raised the energy demands. It has
been estimated that the energy requirement has been increased 17 folds in previous
century (Demirbas, 2007). Furthermore, the emission of greenhouse gases i.e. CO2,
CO, NO2 and SO2, resulted in an increase in air pollution and led to global climate
change (Fuglestvedt et al., 2000). Today, the ecofriendly biofuel utilization as a
substituent for the petroleum based products, has attracted worldwide interest for its
production at large scale because it can be used in current unmodified engines by
blending it with fossil fuels in different proportions (Macedo, 1998; Hansen et al.,
2005). In order to create more sustainable and economically viable system, it is more
important to emphasize on cheaper ways to produce biofuel to make it more favorable
as compared to petroleum based products (Zabed et al., 2014). Various efforts are
being done in this regard to search a renewable source of energy. Recently, biofuels
are considered as an efficient renewable alternative energy source that can easily be
produced by various biological sources i.e. animal, plants, microorganisms etc.
(Aristidou and Penttilä, 2000; Zaldivar et al., 2001).
2.1. Types of Biofuels
Biofuels can be produced in variety of forms to fulfill various energy requirements
(like petroleum products). Some important types of biofuels are:
2.1.1. Biodiesel
Biodiesel consist of short chain alkyl ester, which are formed by transesterification
reaction of vegetable or animal fats (Stevens and Verhé, 2004). Edible oils are usually
not used as fuel; however, the low quality oil is converted into biodiesel that is later
processed and separated from water to be used in engines. The biodiesel can be used
in pure form (B100), or it can be blended with conventional petroleum based biodiesel
to be used in engines (Tickell and Tickell, 2003).
2.1.2. Bioalcohols
Bioethanol is the most commonly used bioalcohols, which can be used in substituent
to gasoline (Huang and Ragauskas, 2012), while other less common bioalcohols are
biomethanol, biopropanol and biobutanol (Minteer et al., 2011). Different types of
bioalcohols are mainly produced by variety of microorganisms, during the process of
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fermentation (Wyman and Hinman, 1990). Sugar rich feedstock i.e. sugarcane juice,
fruits juices, molasses are widely used for the production of bioethanol by the process
of alcoholic fermentation. However, starch containing plants (e.g. cassava, sweet
potato, corn) are first subjected to react with amylase enzymes for the conversion of
starch in to simple monomeric sugars, which are subsequently fermented for the
formation of bioalcohols (Ziska et al., 2009). The production of bioethanol from
lignocellulosic wastes i.e. bagasse, miscanthus, pinus, wheat stalks etc. requires
various pretreatments (physical, chemical or biological). The pretreated biomass then
undergoes enzymatic hydrolysis (by cellulases and hemicellulases) to breakdown
complex fibers to release simple monomeric sugars (i.e. glucose and xylose), which
are later fermented to produce bioethanol (Ragauskas, 2014).
2.1.3. Biogas
For the production of biogas, various energy crops and biodegradable waste (like
manure) is fed in to biodigester, and anaerobic digestion is carried out by using the
consortium of various anaerobic microbes (e.g. acetogens and methanogens). Methane
gas is recovered at the end of reaction from biodigester and used as biofuel. However,
the solid byproduct recovered at the end of process can be used as fertilizers
(Sreekrishnan et al., 2004; Amon et al., 2007; Taherzadeh and Karimi, 2008).
2.1.4. Syngas
Syngas is produced by combination of three processes i.e. pyrolysis, combustion and
gasification. The pyrolysis converts the biofuel into carbon monoxide. Little oxygen
is provided to support combustion. The gasification converts further substrate into
carbon monoxide and hydrogen. The syngas is a better fuel than combustion of
original biofuel because of more content of energy present in syngas (Basu, 2010;
Göransson et al., 2011).
2.2. Generations of Biofuels
On the basis of type of substrate, processing technology and their level of
development; biofuels are categorized into various generations (Nigam and Singh,
2011).
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2.2.1. First Generation biofuels
First generation biofuels are usually produced from sugar containing crop (i.e.
sugarcane juice, sugarbeet, molasses); starch containing crops (i.e. cereals, grains);
vegetable oils, animal fats etc. (Naik et al., 2010; Havlík et al., 2011).
2.2.2. Second Generation Biofuel
Second generation biofuel uses non-food substrate to produce biofuel. The substrate
utilized for second generation are stalks of wheat, corn, wood, sugarcane bagasse or
energy crops (miscanthus or bagasse). The second generation biofuel avoids food vs.
fuel debate by utilizing nonfood crops for the production of bioethanol. It usually
utilizes lignocellulosic materials which are degraded by various pretreatments and
degrading enzymes to convert complex structure into simple monomeric sugars,
which can be subsequently converted into variety of biofuels. Many second
generation biofuel i.e. biohydrogen, biomethane, biodiesel are under investigation
(Naik et al., 2010; Sims et al., 2010; Havlík et al., 2011).
2.2.3. Third Generation Biofuel
Algae are considered as low input high output feedstock to generate third generation
biofuels. In comparison to land crop like soybean, it is able to produce 30 times more
energy per acre. The most promising advantage of algae biofuel is its
biodegradability, which makes it environmentally safe option. Second and third
generation biofuels are termed as advanced biofuels (Dragone et al., 2010; Maity et
al., 2014).
2.2.4. Fourth Generation Biofuel
The fourth generation biofuel is attempting to convert vegetable oil and biodiesel into
gasoline. Another famous company ―synthetic genomics‖ is trying to produce biofuels
directly from carbon dioxide. Some researchers are trying to produce those genetically
modified crops that may able to consume more amount of carbon dioxide than
released by the biofuels thus creating an idea of carbon negative fuel (Demirbas,
2009; Lü et al., 2011).
2.3. Bioethanol as Fuel
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Ethanol can be used for variety of purposes like solvent, paints, perfumes and
beverage; however, recent investigations have revealed its importance as a biofuel
that can be used in substituent to gasoline (Wyman and Hinman, 1990; Alfenore et
al., 2004). Ethanol used in vehicles can either be a pure form (E100), or it can be
blended with various proportion of gasoline. The commonly used ethanol blends are
E5, E10, E25 and E85, where the letter ―E‖ describes the percentage of ethanol with
in ethanol-gasoline blend e.g. E5 contains 5% ethanol with 95% of gasoline. The
modern vehicles can use the ethanol-gasoline blend up to E15; however, there are
specialized vehicles which can run on any type of the ethanol blend and are known as
―Flex-fuel vehicles‖ (Suarez-Bertoa et al., 2015).
2.3.1. Production of Bioethanol
Bioethanol can be produced by variety of methods that include synthetic method or
biological method. Nowadays, the ethanol that is utilized as a solvent (or non-
beverage purposes) is usually produced by acid-catalyzed hydration of a
petrochemical feedstock i.e. ethylene. The ethanol produced by this method is termed
as ―synthetic‖ (Gnansounou and Dauriat, 2005)
C2H4 + H2O CH3CH2OH
Ethylene Water Ethanol
Ethanol is produced by biological method (fermentation), when it has to be used in
beverages or biofuel. One of the most common yeast being used in this process is S.
cerevisiae. The overall process was explained by scientist Gay-Lussac, who formed
the basis to calculate fermentation efficiency.
C6H12O6 2C2H5OH + 2CO2
Glucose Ethanol Carbon dioxide
(1 Kg) (0.511 kg) (0.489 kg)
During this process 1 kg of sugar is converted into 0.51kg of ethanol and 0.49kg of
CO2 (Gnansounou and Dauriat, 2005).
2.3.2. Role of Substrate
The nature and type of the substrate has immense importance for the production of
bioethanol (Prescott et al., 2002). Substrates are mainly categorized into three types
i.e. sugar containing substrate, starch containing substrate, and lignocellulosic waste.
There are varieties of feedstock which are rich in sugars like fruit juices, sugarcane
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juice, sugarcane molasses etc., and they can easily be converted into bioethanol by the
process of fermentation (Nigam, 1999). Other important substrates used for this
purpose are sweet sorghum (Bulawayo et al., 1996), sugar beet and beet molasses (El-
Diwany et al., 1992; Agrawal and Kumar, 1998).
Some other easily fermentable substrates are cheese whey and milk; however, those
microbial strains can be used to utilize these substrates which have the ability to
hydrolyze lactose (Ghaly and Ben-Hassan, 1995; Silva et al., 1995). Starch containing
substrates can also be used for the production of bioethanol. Most common among
them is corn, which is utilized by USA (the top ethanol producer) for the production
of bioethanol. Other starch containing materials are sweet potato and wheat, which are
also reported for the production of bioethanol by using various microbial strains
(Lindeman and Rocchiccioli, 1979; Maisch et al., 1979; Sree et al., 2000).
Recently, many researchers are working on the production of bioethanol from
lignocellulosic wastes, which may include woods, grasses, agricultural feedstock etc.
(Taherzadeh and Karimi, 2008). Different enzyme companies are trying to enhance
the production of various hydrolyzing enzymes i.e. cellulase and xylanases by
designing genetically modified organisms. The reduction in enzyme cost will reduce
the cost of overall process (Kaar and Holtzapple, 2000; Sun and Cheng, 2002; Yu and
Zhang, 2004). Pineapple, Cocoa and sugarcane bagasse are being tried to use for the
production of bioethanol, however this is very expensive process to convert them into
bioethanol (Samah et al., 1992). Many researches are being done to make this process
economically feasible to commercialize.
2.4. Bioethanol Production from Sugarcane Molasses
Molasses is actually a thick, dark brown; honey like material that can be obtained
from the sugarcane juice, after the sugar has been crystallized. Different types of the
sugars are present in sugarcane molasses e.g. glucose, sucrose, fructose that constitute
about 45-60% of the total sugar. Sugarcane molasses also contains nitrogen which is
important for the generation of amino acid and proteins in fermenting microbes (W
Borzani et al., 1993; Walter Borzani, 2001). Different investigations are being done
for the production of bioethanol by using free and immobilized microbial cells (Gikas
and Livingston, 1997; Yamada et al., 2002). As molasses contains easily fermentable
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sugar; therefore, no specific pretreatment is required to convert it into ethanol. Brazil,
the second major ethanol producer among the world, utilizes sugarcane juice and
molasses for the production of bioethanol (Bose and Ghose, 1973; Morimura et al.,
1997; Agrawal and Kumar, 1998). Similarly molasses is also utilized in India and
Pakistan for same purpose (Sharma and Tauro, 1986; Bulawayo et al., 1996).
Moreover, in India and Pakistan, sugarcane molasses is very cheap and plenty;
therefore, they prefer to utilize this easily fermentable substrate for the production of
bioethanol (Sharma and Tauro, 1986).
2.4.1. Role of Microorganisms
An extensive research has been carried out on various types of microorganisms i.e.
bacteria, fungi or yeast, which have been involved in process of alcoholic
fermentation (Bajaj et al., 2001). Among various microbes, S. cerevisiae has been
considered as the most efficient strain for the production of bioethanol. Other
important yeast strains that have been used in industry for the production of
bioethanol are Shizosaccharomyces pombe; Saccharomyces uvarum;
Zygosaccharomyces spp; Saccharomyces ellipsoideus; and Kluyveromyces (Walker,
1998; Canilha et al., 2012). Among the bacteria, the most promising specie that has
been studied for the enhanced production of bioethanol is Zymomonas mobilis.
Skotnicki et al., (1981) studied the ethanol yield by using 11 different strains of Z.
mobilis, and reported that some of these bacterial strains were tolerant against high
sugar and ethanol concentration. Moreover, these strains also showed stability at high
temperature condition. Bertolini et al., (1991) isolated a strain of S. cerevisiae and
allowed it to grow at 48% sugar concentration, and reported the fermentation
efficiency of 89 to 92%. However, in a comparative study, Bansal and Sing (2003)
reported that S. cerevisiae exhibited better ethanol production from sugarcane
molasses as compared to Z. mobilis. The main reason for different level of production
by using various strains was difference in metabolic pathways acquired by these
strains. The enzymatic study of these microbial strains showed the presence of
specialized enzymes (i.e. invertase and zymase) in these strains, for the production of
bioethanol. Invertase is involved in conversion of sucrose in to reducing sugars which
is subsequently fermented to ethanol with the help of zymase enzymes. Moreover, it
was observed that each microbe performs its best at specific physicochemical
conditions. At extreme conditions, the enzyme activities are reduced which adversely
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Enhanced production of biofuel from sugar industry waste Page 16
affects the efficiency of microbial strain for the production of bioethanol
(Gnansounou and Dauriat, 2005).
Genetically Modified Organisms
Two of the main enzymes responsible for the production of bioethanol are pyruvate
decarboxylase (PDC) and alcoholic dehydrogenase (ADH). These enzymes are found
in Z. mobilis as well as S. cerevisiae; however, Z. mobilis showed more affinity
towards substrate and S. cerevisiae has been shown more tolerance against ethanol
(Gunasekaran and Raj, 1999; Matthew et al., 2005). Therefore, the Plant
Biotechnology Unit of the Corporación para Investigaciones Biológicas (CIB)
genetically modified S. cerevisiae by inserting two main genes from Z. mobilis i.e.
pdc and adhII. As a result, the engineered strains exhibited better ethanol yield as
compared to parental strain i.e. CBS8066, when glucose was used as carbon source
(Vásquez et al., 2007; Peña-Serna et al., 2011).
2.4.2. Ethanol Tolerance
One of the main hurdles faced by fermenting microbes is their intolerance against
high concentration of ethanol, which reduces the final ethanol concentration. High
ethanol content denatures proteins and necessary enzymes, thus hinders the process of
fermentation. It has been observed that baker’s yeast can’t tolerate the ethanol more
than 5-6% (v/v); however, 12-15% (v/v) ethanol production is common in wine
industries. It has been reported that those strains which are used in alcohol industries
are tolerant up to 18% (v/v) ethanol (Balat and Balat, 2009).
2.4.3. Physicochemical Pretreatments
The main problems faced by ethanol industry are the lower ethanol yield and
fermentation efficiency, which are usually attributed to low ethanol tolerance among
fermenting microbe. Second major reason of these problem is operating the process
under non-favorable physicochemical parameters i.e. sugar concentration, pH,
temperature, inoculum etc. (Wyman and Hinman, 1990).
(a) Effect of Sugar Concentration
In ethanol industries, increase in sugar concentration is one of the best way to enhance
the production of bioethanol; however, too high concentration inhibits metabolic
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Enhanced production of biofuel from sugar industry waste Page 17
pathway of fermenting microbe (Jones et al., 1994). It has been observed that the
increase in amount of sugar concentration creates high osmotic pressure that is
difficult to be tolerated by microorganisms, thus affects fermentation efficiency.
Bertolini et al., (1991) isolated various strains from Brazilian ethanol industries and
studied their osmotic tolerance. Some of the yeast strains were able to utilize 30%
sugar concentration and produced various amount of ethanol in fermentation media.
Borzani et al., (1993) studied the logarithmic relationship between initial sugar
concentration and fermentation time and found that microbes withstand increase in
sugar concentration up to certain limit; further increase in sugar concentration
adversely affects fermentation process. Sree et al., (2000) used various sugar
concentrations i.e. 150, 200 and 250 (gm/l) at 30°C and studied that the final ethanol
yield obtained by these concentration was 72.5, 93 and 83 (gm/l), respectively at 30ºC
after 48 h. Periyasamy et al., (2009) revealed that under optimized condition, S.
cerevisiae strain produced 6.7% (v/v) of ethanol when 30% (w/v) of sugar was
present in fermentation medium. In another study maximum ethanol production was
determined as 7.7% (v/v) from 16% (w/v) sugar containing fermentation medium
(Arshad et al., 2008).
(b) Effect of pH
In order to obtain high ethanol yield from fermentation medium, the adjustment of pH
to the optimal value is quite important. The pH range 4-5 is considered as the optimal
range for most of the fermenting yeasts. The pH adjustment is important to avoid
bacterial growth by providing acidic environment because Lactobacilli, the main
contaminants of fermentation media prefer to grow at pH 5.4 to 5.6; furthermore,
fermenting yeast showed better growth at slightly acidic pH (Mathewson, 1980). The
studies showed that the growth of contaminants in a medium produces undesirable
compounds in fermentation medium, which makes the environment unfavorable for
other microbes (Yadav et al., 1997; Periyasamy et al., 2009). The optimum pH of
different yeast varieties was studied by many researchers and all reported same range
for optimum pH i.e. 4-5, when yeast was used for alcoholic fermenting (Lin and
Tanaka, 2006; Mariam et al., 2009; Maharjan et al., 2012). It was studied by Wang et
al., (2001) that the contamination of acetic acid bacteria increases at pH above 7.
Moreover, it also affected aldehyde dehydrogenase activity, which stops alcoholic
fermentation and enhanced glycerol production.
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(c) Effect of Temperature
In order to obtain the desired amount of product, it is important to monitor the
temperature, as it is one of the important factors that alters the rate of process and
directly affects the final yield. During the process of ethanol production, heat is
evolved from the fermentation process which increases the temperature of reactor;
due to these reasons, the fermenter should be cooled down frequently to maintain the
temperature at the optimum level. The increase in temperature adversely affects the
viability of microbial cells and metabolic process. It has been investigated that high
temperature alters the fatty acid composition in yeast cell membrane (Ohta et al.,
1988). The change in phospholipid content in cell membrane affects membrane
fluidity and cellular activities (Banat et al., 1998). At higher temperature, decrease in
ethanol yield might be attributed to protein denaturation which hinders enzyme’s
catalytic activity and cause death of yeast cells (Dhaliwal et al., 2011).
(d) Nutrient Requirement
It was previously believed that the ethanol tolerance is not affected by nutritional
requirement; however, with the advent of research this concept has been changed
(Casey et al., 1983). Now, the studies have been shown that the addition of
nitrogenous source like urea in fermentation medium not only enhances ethanol
tolerance, but also improves sugar utilization competences of fermenting microbes.
For better fermentation, urea was commonly added in fermentation media as nitrogen,
whereas DAP (Diammonium hydrogen phosphate) as phosphorus plus nitrogen
source. Nitrogen is important for amino acid synthesis, while phosphate has major
role in glycolytic pathway during fermentation and also involves in nucleic acid
synthesis, thus plays vital role in yeast replication (Mukhtar et al., 2010). Nofemele et
al., (2012) reported in his studies that 2g/l of urea addition has been shown to enhance
the ethanol concentration up to maximum level when fermentation was carried out at
35ºC. Other researchers has been shown the similar effect that the addition of urea and
DAP both played important role to enhance ethanol yield. Mukhtar et al., (2010)
studied effect of nitrogen on a commercial yeast i.e. Saf-instant and determined
similar increase in ethanol yield, when either urea or DAP was added. Maharjan et al.,
(2012) evaluated the effect of various nitrogen sources such as urea, ammonium
PhD Thesis
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sulfate, di-ammonium phosphate, ammonium chloride and ammonium nitrate to select
the best option for enhanced ethanol production by using yeast strain S2Y8.
(e) Effect of Chelating Agents
Molasses contains many metals and heavy metals like iron (Fe), aluminum (Al),
copper (Cu) etc., which can hinder the activity of fermenting microbes and reduces
final yield. Many scientists have studied the effect of various chelating agents to
remove the metals from fermentation media. Lee et al., (2012) studied the effect of
EDTA (ethylene diamine tetra acetic acid) and NTA (nitrile tri-acetic acid) for
adsorption of metal ions present in media and also studied the effect on enhanced
ethanol production by using L. japonica as fermenting strain. Benerji et al., (2010)
used EDTA and sodium potassium tartrate in different concentrations to study their
effects on ethanol production from muhua flower. Pandey et. al., (1993) studied the
concentration ranges from 50 mg/L to 2000 mg/L of various chelating agents i.e.
EDTA, potassium ferrocyanide (K4Fe(CN)6,) and sodium potassium tartrate on
production of ethanol from sugarcane molasses.
(f) Effect of Inoculum
In general large amount of cells at their exponential phase are required to make the
process of fermentation successful. Many scientists have previously studied the effect
of inoculum on enhanced production of bioethanol. Munene et al., (2002) reported
that the inoculum size of 7×106 viable count/ml yielded maximum ethanol with
minimum byproducts i.e. glycerol. Laopaiboon et al., (2007) reported that 1x108
cells/ml was the optimized inoculum size for maximum ethanol production. Later,
Perisyasmi et al., (2009) during his study on S. cerevisiae revealed that 2 g of yeast
inoculum exhibited maximum production of bioethanol. Benerji et al., (2010)
determined that 1.5% (v/v) of 48 h old inoculum was best for the maximum
production of bioethanol.
2.5. Types of Fermentation
2.5.1. Batch Fermentation
During batch fermentation, the fermenter is filled with substrate, then pH and
temperature of the system is adjusted according to the optimized conditions.
Moreover, nutrient supplements are added to meet the growth requirement of
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fermenting microbes. The substrate is steam sterilized before the addition of inoculum
in fermenter. The process of fermentation is completed after certain time and the
entire fermentation medium is removed for the product recovery. Melle-Boinot
process is also a type of batch fermentation, during which the substrate is first
sterilized and pH is adjusted by the addition of H2SO4. The dissolved solid content of
fermentation broth is adjusted between 14-22°brix. After completion of fermentation
process, the medium is centrifuged to separate ethanol and yeast. Yeast cells are then
recycled to the same fermenter for next cycle in order to obtain maximum
fermentation efficiency by maintaining elevated cell concentration (Kosaric and
Velikonja, 1995). One of the major limitations associated with batch fermentation is
that it requires higher concentration of sugar for higher ethanol yield; however, high
sugar concentration inhibits the process due to osmotic intolerance of most of the
yeast strains (Grubb and Mawson, 1993). Moreover, there is also accumulation of
ethanol at the end of process that adversely affects the growth of yeast, thus hinders
the process for further ethanol production (Lynd et al., 1991).
2.5.2. Fed-Batch Fermentation
Due to osmotic intolerance of fermenting strains, fed batch fermentation was
introduced. Fed batch fermentation is a semi-batch fermentation, in which substrate
and necessary nutrients are added either continuously or intermittently. The product is
recovered at the end of the fermentation process, either fully or partially. This process
can be repeated several times if the microbial cells are fully viable. During fed batch
fermentation the volume of fermentation medium increases during the course of
reaction. Fed batch fermentation avoids the problem of high sugar intolerance of
fermenting strain because it allows the stepwise addition of substrate in fermenter
(Yamanè et al., 1984). By manipulating the feeding rate, the nutrient addition can be
manipulated to remain constant or increased at predetermined optimal rate. This type
of fermentation is usually used in Brazil for the production of high concentration of
ethanol from sugarcane molasses (Minihane and Brown, 1986).
2.5.3. Continuos Fermentation
Continuous fermentation is the process that makes it possible to produce ethanol
continuously for unlimited period of time (Klapatch et al., 1994). The substrate is
continuously added to the fermenter and ethanol is continuously removed, which
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removes the problems created in fermentation medium because of high concentration
of substrate or product. The number of microbial cells is also adjusted to the constant
number in fermenter by continuous removal of worn out cells (Hack et al., 1994;
Banat et al., 1998).
The major limitation of the continuous fermentation for the ethanol production is the
supply of oxygen. A continuous supply of oxygen is required for the growth of cell
and biomass generation; however, the process of fermentation requires anaerobic
conditions. During ethanol production, lower availability of oxygen makes it difficult
to generate energy cells to replace the worn out old cells. Further research is still
required to overcome these limitations (Banat et al., 1998).
Continuous fermenter mainly consists of series of tanks: the first tank ―wort receiver‖
dilutes the wort to adjust specific gravity of fermentation medium, which opens into a
hold up vessel. The holdup vessel mixes new wort with yeast and the recycled wort
coming from the first fermenter. The holdup fermenter is followed by first fermenter
(residence time 30 h), second fermenter (residence times 12 h) for final tuning, and
yeast separator. The yeast separator separates the yeast from this system by
centrifugation (Boulton and Quain 2001).
2.6. Bioethanol Production from Sugarcane Bagasse
Sugarcane bagasse is one of the major byproducts of sugar industry, which is
lignocellulosic in nature and mainly consists of cellulose, hemicellulose and lignin.
This industrial waste is broken down to sugars (i.e. glucose and xylose) by various
pretreatment strategies, which is subsequently converted to various types of fuels i.e.
bioethanol, biogas, biobutanol etc. (Maitan-Alfenas et al., 2015)
2.6.1. Chemical Composition of Sugar cane Bagasse
Lignocellulosic material mainly consist of three types of polymers i.e. cellulose (30-
50%), hemicellulose (15-30%) and lignin (10-25%); however, the composition of
these three constituents vary with the type of plants (Monlau et al., 2013). In addition,
small amount of pectin, proteins and non-structural carbohydrates (i.e. sucrose,
glucose and fructose) are also present in lignocellulosic biomass (Jørgensen et al.,
2007).
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Fig. 2.1. Chemical composition of lignocellulosic biomass (Scheller and Ulvskov,
2010)
(a) Cellulose
Cellulose is considered as the main constituent of cell wall. It is linear polysaccharide
polymer of glucose that is linked together by β-(1→4) glycosidic bonds (Fengel and
Wegener, 1984; Fengel, 1992). The nature of these bindings allows the cellulose
polymer to arrange in linear chains. The chemical formula of cellulose is represented
as (C6H10O5)n, and the different chemical properties of cellulose depends on its degree
of polymerization that ranges from 500 to 15000 (Holtzapple et al., 1990). The inter
and intra-molecular hydrogen bonding helps in formation of various parallel chains
that are coalesced to form micro-fibrils, which are further united to constitute a fiber
(Faulon et al., 1994; Chandra et al., 2012). This highly organized structure makes
cellulose surface highly hydrophobic and tensile, which is resistant to organic solvents
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and enzymatic hydrolysis (Ward et al., 1989). The hydrophobicity of cellulose
molecule makes a thick layer of water that makes the diffusion of enzymes more
difficult (Matthews et al., 2006).
In plant cell walls, cellulose can be found as either crystalline, amorphous or both
forms. The intra and inter-molecular hydrogen bonding with in cellulose structure
constitutes 36 chains that aggregate to form crystalline structure (Matthews et al.,
2006). It is suggested that 36 glucan chains constitute elementary fiber of cellulose.
The most inner six chains are truly crystalline that are surrounded by 12 para-
crystalline chains. However, the outer shell of the cellulose fiber contains 18 chains
which are amorphous in nature (Ragauskas, 2014).
It is considered that, the enzymes can easily access amorphous regions of cellulose
and hydrolyze it to release glucose. However, the crystallinity of cellulose makes it
difficult to be degraded by enzymatic activity as the contact efficiency of crystalline
cellulose is decreased (Chang and Holtzapple, 2000). During autohydrolysis and
dilute acid pretreatment (DAP), it has been determined that the increase in the
crystallinity of cellulose had adverse effect on efficiency of pretreatment. Thusly, it is
considered that the strategies to remove crystallinity can enhance the digestibility
(Han et al., 1983). Other studies reported that, crystallinity had no effect on
digestibility; rather the increase in digestibility was attributed to increase in pore size,
reduction in degree of polymerization (DP) and particle size (Puri, 1984; Sinitsyn et
al., 1991). All these factors are interlinked that makes it difficult to analyze only one
factor separately. However, due to heterogeneous nature of biomass, crystallinity can
only be considered as one of the important factor that affects digestibility (Taherzadeh
and Karimi, 2008).
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Fig.2.2. Cellulose structure: Crystalline (red); Para-crystalline (green) and amorphous
(blue) chains (http://www.uky.edu/~dhild/biochem/11B/lect11B.html)
(b) Hemicelluloses
―Hemicelluloses‖ is a collective term used to represent various polysaccharides
present in cell wall of plants. These are considered as highly branched structures and
are associated with celluloses. Contrary to cellulose, hemicelluloses have low degree
of polymerization (less than 200) and are mostly amorphous in nature. Hemicelluloses
are mainly composed of pentoses (xylose and arabinose) and hexoses (mannose,
glucose and galactose). In hardwoods and agricultural residues, xylose (C5 sugar) is
the most abundant reducing sugar among hemicelluloses. Xylan has backbone of β-
(1,4)-linked xylosyl residues which is acetylated (Kuhad et al., 1997). Fengel and
Wegener (1984) reported that, the quantity of acetic acid was more in hardwood
feedstock as compared to softwood feed stock. In heteroxylans, residues of xylose are
replaced by other components, and are mostly reported in variety of plants. Grasses
are mainly composed of glucuronoarabinoxylans, which contains glucuronic acid and
arabinose associated with xylan (Carpita et al., 2001; Saha, 2003). Most of the sugar
component of hemicelluloses involves in formation of covalent linkages between
lignin and carbohydrate resulting in formation of lignin-carbohydrate complex (LCC).
Benzyl ester, benzyl ether and glycosidic linkages are the most common LCC
linkages reported in various biomasses. The benzyl ester linkage can be hydrolyzed
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by alkaline treatment; however, the other two remains stable during alkaline treatment
(Ragauskas, 2014).
(c) Lignin
After cellulose and hemicelluloses, lignin is the third most abundant constituent of
plant cell wall, which imparts resistance (against microbes), stability and
impermeability to the cell wall structure. Lignin-carbohydrate complex actually
imparts structural integrity, rigidity and prevent the swelling of biomass. Lignin
adopts various ways like sterical hindered of enzymes and fiber swelling, to make the
digestion of biomass difficult (Mooney et al., 1998). It is a highly branched
amorphous structure consists of coniferyl (guaiacyl propanol), coumaryl (p-
hydroxyphenyl propanol) and sinapyl (syringyl alcohol), which are phenyl propanoic
alcohols with different substituents (Robert, 2003). The abundance of the polyphenyl
propanoic acid depends upon type of specie, maturity and the locality of lignin with in
cell wall. Usually, low lignin content was reported in grasses; however, hardwood has
comparatively higher lignin content (Monlau et al., 2013). Previously, three main
groups of lignin was reported i.e. the lignin from softwood contains guaiacyl units, the
hardwood with guaiacyl and syringyl units and herbaceous plants have all of the
above three units present in varying fractions (Boerjan et al., 2003; Vanholme et al.,
2010). The greater amount of guaiacyl subunits in softwood makes it more
recalcitrant than hardwood which is mainly composed of guaiacyl and syringyl
subunits (Ramos et al., 1992).
It has been reported that lignin was less hydrophilic as compared to celluloses and
hemicelluloses that makes the water absorption and fiber swelling quite difficult
(Fengel and Wegener, 1984; Grabber, 2005; Akin, 2008). The water around 180°C
starts dissolving lignin under neutral conditions; however, the solubility of lignin
under acidic, basic or neutral conditions depends on precursors of lignin i.e. sinapyl,
coniferyl or courmaryl alcohol (Kubikova et al., 1996; Grabber, 2005). Alcohol,
dioxane, acetone, pyridine and dimethyl sulfoxide are usually used to dissolve the
lignin (Ragauskas, 2014). It is also believed that dissolved lignin inhibit cellulases and
xylanases that makes the digestion more complicated (Berlin et al., 2007).
2.7. Pretreatment Strategies
2.7.1. Physical Pretreatments
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(a) Milling
During the process of milling, the biomass is grounded to the final particle size up to
0.2 to 2 mm. The reduction in size makes the substrate more accessible to enzymes by
degrading lignin-carbohydrate complex and also plays an important role in reduction
of crystallinity (Mais et al., 2002). There are different types of millings i.e. ball
milling, hammer milling, two-roll milling, disk milling and colloid milling. The main
bottleneck of this process is the high energy consumption, which can be overcome by
wet disk milling. Da Silva et al., 2010 treated sugarcane bagasse to compare the
effectiveness of ball milling and wet disk milling, and reported 78.7% and 49.3%
glucose yield, respectively.
(b) Irradiation
The ultimate goal of this pretreatment is to enhance the enzymatic hydrolysis. The
irradiations can be either used alone or in combination with other pretreatments. The
irradiations directly affect cellulose component and breakdown the glycosidic bonds
thus generated delicate fibers and oligosaccharides. More specific microwave
irradiation disrupts cellulose by molecular collision and dielectric polarization
(Gabhane et al., 2011). Imai et al., (2004) studied the effect of irradiation on
carboxymethyl cellulose (CMC), and reported the increase in enzymatic hydrolysis of
cellulose by 200%. Kaumakura et al., (1983) reported the doubling of enzymatic
saccharification when bagasse was irradiated with acid pretreatment. Intanakul et al.,
(2003) irradiated the sugarcane bagasse by using water/glycerine as the medium of
action and recovered 50% of carbohydrate as reducing sugar. The major advantage of
this process is short processing time and selectivity; however, the major drawback is
its high cost and difficulty to operate at industrial level (Cheng et al., 2011).
(c) Pyrolysis
During this process, lignocellulosic biomass is heated to temperature above 300°C,
which cause rapid degradation of cellulose into gaseous component and residual char.
At lower temperatures, more volatile compounds are formed because of the low
reaction speed. Fan et al., (1987) reported the digestibility of 85% of cellulose by acid
hydrolysis after mild condition pyrolysis of bagasse. The product of pyrolysis is
directly used as fuel rather than its conversion into bioethanol or biogas. Garc a-
Pèreza, et al., (2002) carried out vacuumed pyrolysis of sugarcane bagasse and
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reported 34.4% oil yield. The bio-oils obtained after vacuumed pyrolysis had low ash
contents and less viscosity, which makes it a potential valuable liquid fuel.
(d) Freeze Pretreatment
This pretreatment has achieved great attention because of its high effectiveness and
environment friendly features. The study of this pretreatment on rice straw has shown
the increase in enzymatic digestibility. A very few studies has been carried out on this
strategy. One of the major bottlenecks of this process is its high energy requirements
(Chang et al., 2011).
2.7.2. Chemical pretreatment
(a) Acidic Pretreatment
Acid has been widely used to convert complex lignocellulosic biomass into easily
degradable structure. Among all acids, most of the studies were carried on sulfuric
acid; however, other acids i.e. nitric acid, hydrochloric acid and phosphoric acid have
also shown positive effect on breakdown of complex structure (Panagiotopoulos et
al., 2012).
The pretreatment of biomass with sulfuric acid converts hemicelluloses into simple
monomeric sugars, thus enhances the accessibility and digestibility of cellulose.
Acidic pretreatment can be carried out at either low acidic condition with high
temperature, or high acidic condition with mild temperature (Taherzadeh and Karimi,
2008). The high concentration acidic pretreatment is an economic process; however,
corrosiveness of equipment, toxicity, acid recovery and degradation of glucose into
furan type inhibitors i.e. HMF (5-hydroxy methyl- furfural) and 2-furfuralaldehyde
makes this process inapplicable (Sun and Cheng, 2002; Almeida et al., 2007; Gírio et
al., 2010; Pedersen et al., 2010). In comparison, dilute acid pretreatment (DAP)
favors over concentrated pretreatment because of ease in its operation. DAP can be
carried out either for short retention time (1-5 min) at higher temperature, or long
retention time (30-90 min) at low temperature condition (Cruz et al., 2000). Moutta et
al., (2012) treated sugarcane bagasse with dilute H2SO4 and reported 90% removal of
hemicelluloses. Moreover, the glucose yield was also enhanced up to 65%. The major
drawback of this pretreatment is the formation of various types of inhibitors i.e. furan,
carboxylic acid and phenolic compounds. At higher temperature, glucose is degraded
into hydroxymethylfurfural (HMF); whereas xylose is degraded into furfural which is
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further degraded into levulinic acid and formic acid, respectively. All these inhibitors
may affect subsequent downstream phases that include enzymatic hydrolysis and
fermentation (Palmqvist and Hahn-Hägerdal, 2000). The pH of the process should be
monitored appropriately to reduce the formation of inhibitors. Another drawback
associated with the acidic pretreatment is its high cost which is mainly attributed to
neutralization of the process media. The neutralization of the media is important to
carryout subsequent enzymatic hydrolysis and fermentation (Taherzadeh and Karimi,
2008).
(b) Alkaline Pretreatment
For alkaline pretreatment of biomass, various studies on effect of sodium hydroxide
(NaOH), potassium hydroxide (KOH), calcium hydroxide (CaOH2), and ammonia
(NH3) pretreatment have been investigated (Wan et al., 2011). This method is
believed to increase the porosity of biomass by saponification and salvation reaction
involved in disrupting the linkages between hemicelluloses and other components of
biomass and induces the swelling of celluloses (Sun and Cheng, 2002). It has also
been studied that the ester bond linkages between lignin and xylan layers are
disrupted during alkaline pretreatment, thus helps in delignification of lignocellulosic
biomass. Zhao et al., (2010) pretreated sugarcane bagasse with 10% NaOH and
reported 96% of delignification and fiber swelling after pretreatment. The major
advantages associated with alkaline pretreatment are removal of acetyl group, lignin
and different uronic acid substitutions, which hinders the accessibility of cellulose to
hydrolytic enzymes (Li et al., 2010). However, the effect of this pretreatment on
solubilization of cellulose and hemicellulose is much weaker as compared to acid
pretreatment (Carvalheiro et al., 2008). Other advantages related to alkaline
pretreatment are requirement of low temperature to operate this process. Furthermore,
this pretreatment doesn’t require specialized corrosion resistant reaction equipment
(Digman et al., 2007). The major drawback associated with this pretreatment is
prolonged residence time from few hours to many days, and also the need of
neutralization for the subsequent enzymatic hydrolysis and fermentation process
(Wan et al., 2011).
(c) Organosolvent pretreatment
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In organosolvent pretreatment process; ethanol, methanol, acetone, ethylene glycol
and tetrahydrofuran alcohol is used either in presence or absence of catalyst (Mesa et
al., 2011). Different organic or inorganic acids (HCl or H2SO4) or bases (NaOH, NH3
or CaOH) are used as catalyst (Zhao et al., 2009). This pretreatment is specialized for
the biomass having higher lignin content and involved in disruption of bonds between
lignin and hemicelluloses. This pretreatment can lead to the recovery of pure lignin as
a byproduct which can be considered as an extra advantage of this pretreatment (Mesa
et al., 2011). Mesa et al., (2011) reported that pretreatment of bagasse with 30% (v/v)
ethanol at 195°C for 60 min yielded 29.1% glucose during subsequent enzymatic
hydrolysis. The removal of lignin also helps to greatly enhance the surface area for
enzyme accessibility and cellulose digestion (Koo et al., 2011). The major drawback
of this process is use of highly flammable and volatile solvents which can arise the
problem of pressure adjustment and also the recyclability of these solvent to make the
process economically feasible (Sun and Cheng, 2002) and also to make the process
feasible for subsequent enzymatic hydrolysis and fermentation process. Ethanol and
methanol are usually preferred because of their low boiling point and ease of
recyclability.
(d) Ozonolysis
In this process, ozone gas is used to disrupt lignin and hemicelluloses, which in turn
enhances the cellulose digestibility. Ozone acts as strong oxidant that degrades the
lignin by direct ring cleavage. The important features of ozone, like its solubility in
water and its behavior as a strong oxidant, make it an interesting option to carry out
lignocellulosic breakdown (Balat, 2011). It mainly degrades lignin and releases small
molecular weight components like acetic and formic acids (Williams, 2006). The
main advantages of this process is the activity of ozone in ambient temperature, and
little release of degradation byproducts that can act as inhibitors of downstream
phases (García-Cubero et al., 2009). Travaini et al., (2013) studied the effect of
ozonolysis pretreatment on sugarcane bagasse and found increase in glucose and
xylose yield up to 41.7 and 52.4%, respectively. Only xylitol, acetic, formic and lactic
acid degradation compounds were found, with no detection of HMF (5-
hydroxymethylfurfural) or furfural. The main disadvantages associated with ozone are
its high cost and its high quantity requirement to treat biomass (Sun and Cheng,
2002).
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(e) Ionic Liquid Pretreatment
Ionic liquid pretreatment (IL) is another method of reducing the recalcitrance of
biomass that has recently drawn a great deal of attention because of the unique
physical and chemical properties of ILs that are a very stable class of organic salts
with potential application as ―green solvents‖ (Qiu et al., 2012). The main advantages
of using ILs are related to their non-explosive, non-toxic, environment friendly, low
volatility, good recyclability and general stability under severe reaction conditions (Li
et al., 2010; da Silva et al., 2011; Qiu et al., 2012). IL pretreatment is considered as
an effective pretreatment method as it weakens van der Waals interactions between
cell wall components (Li et al., 2010; Bian et al., 2014). In grasses, the ester linkages
that are formed between lignin and arabinoxylan are disrupted during IL pretreatment
(Li et al., 2010). It is expected that IL pretreatment imparts compositional changes
and interact with the original biomass by hydrogen, ionic and Π-Π interaction in order
to dissolve its components (Karatzos et al., 2012). Anionic moieties of ILs act as
hydrogen ion acceptor and interact with hydroxyl groups present within hydrogen
bonding network of cellulose; however, cations interact with lignin though Π-Π
interaction (Qiu and Aita, 2013; Ninomiya et al., 2015). IL pretreatment causes
dissolution of biomass that can be rapidly precipitated with an anti-solvent and this
prevents reconstruction of crystalline phase of cellulose resulting in the formation of
porous and amorphous cellulose. These effects increase surface area availability for
cellulases adsorption and also increase cellulose digestion (Qiang Li et al., 2009; Qiu
et al., 2012; Bian et al., 2014). For biomass pretreatment, three of the most cited ILs
are imidazoliums i.e. [C4mim][Cl] (1-butyl-3-methylimidazolium chloride),
[C2mim][Cl] (1- ethyl-3-methylimidazolium chloride) and [C2mim][OAc] (1-ethyl-3-
methylimidazolium acetate). All these alkylimidazolium salts have been reported as
most effective agents for lignocellulosics dissolution (Karatzos et al., 2012).
2.7.3. Physicochemical pretreatment
(a) Autohydrolysis
Autohydrolysis is recommended as environmentally benign and clean process (Lei et
al., 2013) which doesn’t require any catalyst or corrosive compounds (Hongdan et al.,
2013). Biomass and water are heated from 130-230ºC for different time periods
(from few seconds to several hours) to carry out this pretreatment (Batalha et al.,
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2015). At high temperature (~200˚C) water has an acidic pH and acquires catalytic
properties which eliminates the requirement of catalyst to disrupt biomass (Mosier et
al., 2005). Auto-ionization of water and ionization of acidic species (uronic acid and
formic acid) at high temperature generate hydronium ions that catalyze the series of
reactions and cause reduction in degree of polymerization (DP) of hemicelluloses and
celluloses by hydrolysis of selective glycosidic bonds (Lee et al., 2009; Batalha et al.,
2015). During autohydrolysis, acetyl groups are released from substituted xylan
chains (along with other organic acids) which act as catalysts to assist in acid-
catalyzed hydrolysis of hemicellulose fraction of lignocellulosic biomass (Huang and
Ragauskas, 2012; Sun et al., 2014; Batalha et al., 2015; Pol et al., 2015). The main
compositional changes observed after autohydrolysis are lignin transformations and
depolymerization of hemicellulose and celluloses into oligomers and monomers due
to very high severity conditions (Batalha et al., 2015). These compositional changes
during autohydrolysis pretreatment create more number of structural changes
including increasing the reducing ends of plant polysaccharides for efficient
exoglucanase activity and hence increased cellulose digestibility (Huang and
Ragauskas, 2012; Hongdan et al., 2013; Batalha et al., 2015). The significant
increase in lignin content after autohydrolysis might be attributed to the removal of
significant amount of hemicellulose while retaining most of the lignin. Some
researchers suggested that the increased lignin content might be due to the
repolymerization of polysaccharides degradation product (such as furfural) and/or
polymerization with lignin, which forms a lignin like material termed as pseudo-lignin
(Li et al., 2007). The pseudo-lignin can also be generated from carbohydrate without
significant contribution from lignin, especially under high severity pretreatment
conditions (Sannigrahi et al., 2011).
(b) Steam explosion pretreatment
During steam explosion pretreatment, saturated steam (under high pressure) is
inserted into a reactor (filled with biomass) that raises the temperature to 160-270°C.
Following gas insertion, the pressure is abruptly reduced that explodes the biomass
with degradation of lignin and hemicellulose (Mabee et al., 2006). The extent of the
biomass disruption depends on particle size, temperature, residence time and moisture
content (Sun and Cheng, 2002). It is believed that, this pretreatment enhances
cellulose crystallinity by converting amorphous portion of cellulose in to crystalline.
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During steam hydrolysis, the acetyl group associated with hemicelluloses generates
acetic acids that help in degradation of hemicelluloses. The removal of hemicelluloses
from the surface enhances cellulose accessibility and enzymatic digestibility (Kabel et
al., 2007). In some cases like pretreatment of softwoods require addition of catalyst
like H2SO4 or SO2 because of low content of acetyl group present in their
hemicelluloses (Mackie et al., 1985). Martín et al., (2002) studied the effect of steam
explosion of sugarcane bagasse impregnated with different agents and found that
H2SO4 impregnated bagasse showed comparatively higher glucose yield i.e. 35%.
This pretreatment strategy can induce the formation of inhibitors; therefore, washing
of biomass is prerequisite before subsequent enzymatic hydrolysis and fermentation
(García-Aparicio et al., 2006). Steam explosion is considered as cost effective
pretreatment due to low energy requirement and high energy efficiency.
(c) Ammonia Fiber Explosion (AFEX)
This process is similar to steam explosions; however, during this process liquid
ammonia is used, and the process is carried out at moderate temperatures (60-120°C)
for less than 30 min with subsequent drop in pressure (Kumar et al., 2009; Bals et al.,
2011). Commonly, 1-2 kg of ammonia is loaded per kg of biomass. Similar to other
alkaline pretreatment, AFEX plays an important role to alter lignin structure. This
strategy doesn’t release the sugars due to low hemicelluloses solubilization; however,
this opens up the lignocellulosic structure (Chundawat et al., 2007). The cost of
ammonia and its recovery affect the price of process; however, ammonia can easily be
recovered (Holtzapple et al., 1992). Krishnan et al., (2010) studied on alkali based
AFEX pretreatment of bagasse and reported that it enhance the cellulose digestibility
up to 85%. He also reported that AFEX pretreatment plays important role in
breakdown of ester bond and other LCC linkages thus enhances cellulose and
hemicelluloses accessibility during pretreatment.
(d) CO2 Explosion
This method is similar to steam and AFEX explosions; however, this involves
insertion of high pressure CO2 into reactor followed by sudden pressure drop (Zheng
et al., 1995). In comparison to other explosive strategy, this technique requires low
temperature and less cost as compared to AFEX. Other advantages are related to its
non-inflammability and non-toxicity (Zheng et al., 1995). CO2 explosion also retains
the properties of acidic hydrolysis by formation of carbonic acid (due to reaction of
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CO2 with water); however, carbonic acid is less corrosive as compared to other acidic
pretreatment. Moreover, due to easy removal of CO2, it doesn’t create any waste or no
further processing is required before downstream enzymatic hydrolysis and
fermentation (Schacht et al., 2008).
2.7.4. Biological Pretreatment
The process of biological pretreatment involves variety of microorganisms to degrade
cellulose, hemicelluloses and lignin. Different studies have been done on brown rot,
white rot and soft rot fungi to degrade lignocellulosic material (Ghose, 1978). These
fungi produce lignin modifying enzyme, lignin peroxidases and manganese dependent
peroxidases which breakdowns the intact lignocellulosic structure by oxidative
reactions (Fan et al., 1987; Malherbe and Cloete, 2002). Brown rot fungi mainly
degrade cellulose; whereas white rot fungi and soft rot fungi degrades lignin and
cellulose. Specifically, White rot fungi is the most prominent fungi for lignin
degradation. Hatakka et al. (1983) studied that 35% of wheat straw was converted
into sugar when it was degraded with white rot fungi i.e. Pleurotus ostreatus;
however, the time required to complete that process was estimated as five weeks.
Keller et al., (2003) studied the effect of pretreatment with Cyathus stercoreus on
corn stover and determined three to five fold increase in digestion during subsequent
enzymatic hydrolysis. Kurakake et al. (2007) studied the effect of two bacteria
Sphingomonas paucimobilis and Bacillus circulans on paper mill waste and
determined 94% sugar recovery. Patel et al., (2007) pretreated sugarcane bagasse with
Phenerochaete chrysosporium and resulted in high amount of sugar obtained. He also
pretreated sugarcane bagasse with Aspergillus awamori and Pleurotus sajor-caju and
high amount of ethanol was obtained. The absence of chemicals and mild conditions
requirement creates the interest of scientists on this type of pretreatment; however,
major drawbacks associated with this pretreatment are slow rate of hydrolysis, due to
these reasons this process is not considered as an economically feasible process.
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Fig.2.3. Separation of cellulose, hemicelluloses and lignin after pretreatment of
lignocellulosic biomass (Mood et. al., 2013)
2.8. Enzymatic Hydrolysis
Enzymatic hydrolysis is an important step between pretreatment and fermentation.
Enzymatic hydrolysis is prerequisite to convert polymeric cellulose and
hemicelluloses into monomeric fermentable sugars. Lignin, acetyl and cellulose
crystallinity are the major factors that makes the process of enzymatic hydrolysis
difficult. Lignin acts as the solid block that hinders the activity of enzymes. Acetyl
group may involve in inhibition of enzymes and microbes. However, crystallinity of
cellulose makes it difficult for enzymes to find the site of adsorption for their function
(Chang and Holtzapple, 2000). Intact lignocellulosic structure is first degraded and
opened by different pretreatments, which is then hydrolyzed into fermentable sugars
during the process of enzymatic hydrolysis.
The hydrolysis mechanism involves three steps i.e. adsorption of enzyme, hydrolysis
of celluloses and hemicelluloses, and desorption. Cellulases are mainly divided into
three types on the basis of their mode of action i.e. endoglucanases, exoglucanases
and β-glucosidases (Philippidis, 1994). During first step of hydrolysis, endoglucanase
acts on amorphous part of cellulose and breaks down intermolecular bonds between
adjacent cellulose chains. Moreover, it acts on glycosidic bonds and creates new ends
at crystalline fractions for exoglucanase activity. Exoglucanase starts acting at the
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ends of cellulose chains and releases cellobiose and also glucose (Zhang and Lynd,
2004). In last step β-glucosidase converts cellobiose into fermentable monomeric
sugar i.e. glucose (Teeri, 1997). Cellulases have been produced by bacteria, plants and
fungi; however, fungi showed better results and some strains of Trichoderma reesei
produced 30g/l of cellulases (Chambel, 2008). The hemicelluloses of lignocellulosic
biomass are also degraded by similar enzymes like xylanases, mannases, arabinases
etc. (Saha, 2003).
Figure.2.4. Simplistic overview of some factors limiting efficient hydrolysis of
cellulose: (1) Product inhibition of cellobiohydrolases by cellobiose (majorly) and
glucose, respectively; (2) Unproductive binding of exoglucanases onto a cellulose
chain. (3) and (4) Hemicelluloses and lignin associated with or covering the
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microfibrils prevent the cellulases from accessing the cellulose surface; (5) Enzymes
(both cellulases and hemicellulases) can be non-specifically adsorbed onto soluble
lignin particles or surfaces; (6) Denaturation or loss of enzyme activity due to
mechanical shear, proteolytic activity or low thermostability (7) Product inhibition of
β-glucosidases by glucose (Jørgensen et al., 2007).
2.9. Fermentation
2.9.1. Separate Hydrolysis and Fermentation (SHF)
SHF is the simplest configuration during which each step is separated and operated at
its optimum conditions. During this process, a small portion of feedstock is used for
enzymatic production and then the whole batch of pretreated biomass is added to
reactor for enzymatic hydrolysis, which is subsequently fermented in a separate
fermenter. In fermenter, microbes convert pentoses and hexoses into bioethanol that is
later separated out by distillation. The major advantage of SHF is related to carrying
out all processes at their optimal physicochemical parameters; however, the main
disadvantage is that the sugar released inhibits enzymatic activity (Goldschmidt,
2008)
2.9.2. Simultaneous Saccharification and Fermentation (SSF)
During SSF, the enzymatic hydrolysis and fermentation process is carried out in same
reactor. The main advantage of this process is the reduction of cost that is related to
the use of separate reactors for hydrolysis and fermentation. Moreover, it also reduces
the possibility of enzyme’s feedback inhibition, which is caused by accumulation of
released sugar as a result to enzymatic hydrolysis (Kim, 2004). During this process,
sugar release is abruptly converted into ethanol; therefore, it also reduces the chances
of contamination. The bottleneck of this strategy is compromised physicochemical
conditions (Goldschmidt, 2008). Enzymatic hydrolysis is usually carried out at 40-
50°C (for common cellulases); whereas, the optimum temperature for fermentation is
around 30°C (Barta, 2011). Therefore, the process is carried out at 35-37°C, which
requires more amount of enzyme to complete hydrolytic process. Recent researches
are being done to develop thermo-tolerant enzymes, which can improve SSF
(Goldschmidt, 2008; Barta, 2011).
2.9.3. Simultaneous Saccharification Fermentation and Co-fermentation (SSFC)
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SSFC also helps to reduce the cost eliminating the need of separate reactor. During
this process, hexose and pentose fermenting microbes are added to convert it into
bioethanol; however, there is the competition between hexoses and pentoses for the
same organism that reduce the overall ethanol yield. Due to this reason this process
could not be applied to industrial scale (Goldschmidt, 2008).
2.10. Biofuel from sugarcane: A solution of Food vs. Fuel Debate
In 2008, due to the international community's concerns regarding rise in food price,
the food vs. fuel debate reached a global scale. A United Nations Special
Rapporteur on the Right to Food, Jean Ziegler named biofuels a "crime against
humanity" (Pedro, 2008), and similar concerns were shown by the World Bank's
President, Robert Zoellick (Elliott and Stewart, 2008). Later, Luiz Inácio Lula
(Brazilian President) gave a strong rejection to these claims by putting all the blame
instead on U.S. and European agricultural subsidies, and said that the problem is
restricted to U.S. ethanol produced from corn. The Brazilian President has also
claimed that his country's sugarcane based ethanol industry has not contributed to the
food price crises (Colitt, 2008). In June 2008, Oxfam released a report, which
criticized rich countries for their biofuel policies and claimed that it is not solving oil
or climate prices, but increasing the problem of food shortage. The report also include
that sugarcane based fuel is most favorable in term of greenhouse gas balance and
cost, whereas rich countries spent $15 million to support biofuels while blocking
sugarcane ethanol (Oxfam, 2008). A World Bank report released on July 2008,
reported that US and European fuels are major cause of increase in food price;
however, sugarcane biofuel did not affect the sugar price (Veja Magazine, 2008). In
July 2008, OECD published a report that agreed with World Bank report and critically
evaluated the limited effect on reduction of greenhouse gas (GHG) emission from the
biofuel generation by US and Europe. However, OECD claimed that biofuel
generated from sugarcane reduces GHG emission by 80% as compared to fossil fuels
(OECD, 2008).
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Chapter 03
Materials and Methods
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On the basis of types of the waste generated by sugar industry, this research was
divided in to two main parts. First part discussed the bioethanol production from
sugarcane molasses, and all these experiments were done in Department of
Microbiology, Quaid-i-Azam University, Islamabad, Pakistan. The second part of this
research focused the bioethanol production from sugarcane bagasse, and it was carried
out at The Department of Chemical and Biomolecular Engineering, The University of
Tennessee, Knoxville, USA.
PART A: ENHANCED PRODUCTION OF BIOETHANOL FROM
SUGARCANE MOLASSES
3.1. PHYSICOCHEMICAL PROPERTIES OF MOLASSES
3.1.1. Determination of Total Dissolved Solids (Brix)
The molasses was obtained from Murree Brewery, Rawalpindi, Pakistan. The total
dissolved solid of molasses (also called brix) was determined with the help of brix
refractometer. For this purpose, 1 g of molasses was added into 100 ml of water (in
500 ml beaker) and stirred with the help of magnetic stirrer bar to get a homogenized
mixture, and then filtered through Whatman filter paper. The temperature of the
solution was kept 20ºC by placing it inside water bath. A drop of solution was placed
on the dark rectangular surface of refractometer and its lid was closed to read the
scale. Final brix of molasses was calculated by multiplying scale reading with dilution
factor. This experiment was repeated in triplicates.
3.1.2. Determination of Specific gravity
To determine the specific gravity of molasses, 5 g of molasses was added into 500 ml
of water and dissolved with magnetic stirrer. After getting homogenized mixture, its
temperature was set at 20ºC in water bath and the solution was poured in to measuring
cylinder. The gravity hydrometer was placed inside the solution and allowed to buoy.
When all the air was removed and gravity hydrometer became centered and vertically
positioned then its reading was determined. The specific gravity was determined in
triplicates. Original specific gravity of molasses was calculated by multiplying the
specific gravity with dilution factor.
3.1.3. Determination of Reducing Sugar
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The reducing sugars in molasses were determined by dinitrosalicylic acid (DNS)
method proposed by Miller (1959). In this method, 1 g of molasses was dissolved in
100 ml of water with the help of magnetic stirrer bar. 1 ml of molasses solution was
taken in a separate test tube and 3 ml of DNS reagent was added. The tube was heated
at 90ºC in water bath for 5 min. The tube was dipped in ice cold water to stop the
reaction, and the optical density (OD) was noted at 540 nm with the help of
spectrophotometer. The OD values were compared with standard glucose calibration
curve formulated by same DNS method to determine the reducing sugar of molasses.
3.1.4. Determination of Total Sugars in Molasses
In sugarcane industry, Lane and Eynon method (1923) was employed for total sugar
determination in sugarcane molasses. To determine the total reducing sugar in
molasses, 5 g of molasses was added into 100 ml of distilled water along with the
addition of 5 ml of HCl in Erlenmeyer flask. The molasses was placed in water bath at
70ºC for 10 min to convert sucrose in to monomeric reducing sugars. After treatment,
NaOH was added to neutralize the solution and volume was increased up to 1000 ml,
after that a burette was filled with this solution. The Fehling’s A solution (12.5 ml)
was mixed with Fehling’s B solution (12.5 ml) in a conical flask and 25 ml of distilled
water was added in it and titrated against molasses dilution (filled in burette) at
boiling temperature until the color faded. A few drops of methylene blue indicator
was then added that turned solution to blue color, which was again titrated against
neutralized molasses dilution until disappearance of blue color and appearance of
brick red precipitates. Fehling’s factor was determined by repeating this titration with
known concentration of standard sugar solution filled in burette.
Sugar Concentration (%) = (Dilution factor × Fehling’s factor) × 100
Titrate value x Weight of sample (g) x1000
3.1.5. Determination of Non-Reducing Sugar
Sucrose is most abundant non reducing sugar in molasses, which doesn’t have
reducing ends to react with DNS reagent. The non-reducing sugar in molasses was
determined by following formula:
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Non-reducing Sugars (%) = [Total Sugar (%) - Reducing Sugar (%)] x 0.95
3.2. ISOLATION, SCREENING AND CHARACTERIZATION OF INDIGENOUS
YEAST STRAINS
3.2.1. Sample Collection
Different variety of fruits was selected for the isolation of yeast strains. Grapes,
Strawberry and Carrot were purchased from local market in Islamabad, Pakistan. Soil
sample was obtained from sugarcane field near Multan, Pakistan.
3.2.2. Sample Processing
The fruits collected from different sources were thoroughly washed with distilled
water to remove any chance of contamination. All the fruits were crushed with mortar
and pistil under sterilized conditions and placed separately in autoclaved reagent
bottles for two days at room temperature.
3.2.3. Isolation
Different varieties of yeasts were isolated by serial dilution of fruits and soil samples.
Crushed fruit’s juice (1 ml) was added in 9 ml of sterilized distilled water in test tube.
This solution was serially diluted in ten other test tubes (containing 9 ml of sterilized
distilled water in each) to make dilutions from 10-1
to 10-10
. All test tubes were
vortexed before next dilution to ensure the equal distribution of yeast cells. Similarly,
1 g of soil was added in 9 ml of sterilized distilled water and serially diluted in similar
fashion. All dilutions were plated on Wallerstein Laboratory Nutrient (WLN) agar
medium by spread plate method and petri plates were incubated at 30ºC for 48 to 72 h
(Appendix A). After incubation different colonies were selected on the basis of
different morphological characteristics and purified on separate WLN medium using
streak plate method.
3.2.4. Quantitative Screening
(a) Inoculum Preparation
All isolated yeast strains were grown on YPD broth. YPD medium was prepared by
mixing 1 g of yeast extract, 2 g of dextrose and 2 g of peptone in 100 ml of distilled
water and autoclaved. About 25 ml of YPD broth was taken in 100 ml Erlenmeyer
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flask and inoculated with a loop full of yeast strain. Same procedure was followed for
all isolated yeast strains and all flasks were incubated at 30ºC on shaker incubator
with 100 rpm. After 24 h, yeast cultures were used as inoculum for quantitative
screening (i.e. ethanol tolerance test) to select a comparatively better strain for
enhanced ethanol production.
(b) Ethanol Tolerance Test
Quantitative screening was done by determining tolerance of each isolated strain
against 10% and 15% ethanol concentration. For each yeast strain a set of two 250 ml
Erlenmeyer flasks with 50 ml YPD broths was prepared containing 10% and 15%
ethanol. All these sets of flasks were inoculated with 1 ml of 24 h old culture of their
respective strain and incubated at 30ºC for 72 h. Optical density was measured at 600
nm with spectrophotometer after every 24 h. The most ethanol tolerant strain was
selected for further study.
3.2.5. Identification of Selected Yeast
The selected strain was identified on the basis of morphological and molecular
characteristics.
3.2.5.1. Morphological Identification
The most ethanol tolerant strain was grown in WLN agar media and its morphology
was studied on plates after 48 h of growth. The texture, color and surface of colony
were examined. The microscopic examination of selected yeast was also carried out
by preparing slide in saline solution (0.9% NaCl) and yeast cells were examined by
using 100x magnification.
3.2.5.2. Molecular Characterization
(a) DNA Extraction
DNA isolation was carried out with a little modification in phenol chloroform
method. Selected yeast strain i.e. MZ-4 was cultured in YPD broth for 24 h, and then
1.5 ml of the yeast culture was taken in eppendorf and centrifuged for 5 min at 14000
rpm. Supernatant was removed and 400 µl distilled water was added into pellet along
with 200 mg of glass beads. In addition, 300 µL of 0.1M phosphate buffer, pH 8.0
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(Sigma-Aldrich); 300 µL of 50mM sodium acetate (Sigma-Aldrich); 50 µL Sodium
dodecyl sulfate solution alkaline solution (Sigma-Aldrich); 10mM EDTA (Sigma-
Aldrich), pH 5.5; 400 µL phenol–chloroform–isoamyl alcohol (25:24:1), pH 8.0
(Sigma-Aldrich) was added in the eppendorf and vortexed for 2 min and then it was
placed in ice bath for 3 min. The eppendorf was then centrifuged at 14000 rpm for 15
min and supernatant was collected which was washed once with phenol-chloroform-
isoamylacohal (25:24:1) and afterwards with chloroform-isoamyl alcohol (24:1).
Again supernatant was collected and double the amount of absolute alcohol was
added into it and placed it overnight at -20ºC to precipitate out DNA. Next day it was
again centrifuged at 14000 rpm for 10 min and pellet was washed with 80% alcohol
and dried afterwards. The DNA pellet collected at the end was dissolved in 100 µL of
1x Tris EDTA Buffer and stored at -20°C for further use.
(b) PCR Amplification
Using primers ITS1 50-TCCGTAGGTGAACCTGCGG-30 and ITS4 50-
TCCTCCGCTTATTGATATGC-30, the DNA fragments of the ITS1, 5.8S RNA, and
ITS2 regions were amplified by PCR. PCR reactions were carried out in an AB 2720
thermal cycler (USA) with controlled amplification conditions i.e. initial denaturation
at 94oC for 5 min, followed by 30 cycles of denaturation at 94
oC for 30 s, annealing at
55oC for 30 s, extension at 72
oC for 1 min, and the final extension at 72
oC for 10 min
(White et al., 1990).
(c) Sequence Analysis
For molecular determination of yeast strain, 18S rRNA sequence of isolated DNA
was determined and provided by Macrogen Seoul Korea which was then examined
through nucleotide blast programs of NCBI (National center for biotechnology
information) to determine the homology against partial sequencing of 18S rRNA
(Appendix B).
(d) Phylogenetic Analysis and Submission to Gene Bank
The nucleotide blast program ―Blastn‖ was used for searching the homology against
the partial 18S rRNA sequences. The sequences from NCBI gene bank, having
maximum score and percentage for sequence homology were retrieved, and
alignment of these sequence were done by Molecular Evolutionary Genetic Analysis
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(MEGA) program version 6.06. These sequences were later submitted to NCBI gene
bank where it was assigned by accession number.
3.3. SELECTION OF BEST COMMERCIAL YEAST STRAIN TO COMPARE
WITH BEST INDIGENOUS YEAST STRAIN
3.3.1. Source of Commercial Strains
Four commercial strains of S. cerevisiae were compared with newly isolated
indigenous strain (MZ-4) to determine the most efficient strain for enhanced
production of bioethanol from sugarcane molasses. Rossmoor strains has already been
reported to be used in baking industry (Sultana et. al., 2013) and purchased by local
market in Islamabad, Pakistan. Saf instant was purchased from local vendor in
Islamabad, Pakistan while Uvafem-43 was provided by Murree Brewery, Rawalpindi,
Pakistan and both these strains has been reported for alcohol production from various
sources (Bechem et. al., 2007; Schmidt et. al., 2011). Lalvin EC-1118 was Canadian
strain, and famous for Champaign production from grapes (Valero et al., 2005 and
Carreto et. al., 2008).
3.3.2. Maintenance of Cultures
All the yeast strains selected for study were maintained by culturing on YPD agar
medium. The commercial strains were first added in autoclaved water (1:2 yeast to
water ratio at 30ºC) and after 10 min it was streaked on YPD agar plate. Self-isolated
strain MZ-4 was also transferred from WLN to YPD. All plates were incubated at
30ºC for 48 h and then transferred to refrigerator for preservation.
3.3.3. Strain Activation and Inoculum Preparation
A standard method used in most of brewing industries for inoculum preparation
before ethanol fermentation was followed. Sugarcane molasses dilution having 1.030
sp.grv (5% sugar conc) was prepared by distilled water with the help of gravity
hydrometer. Low gravity dilutions were prepared to prevent the strains from adverse
effect of high osmotic pressure which could be created due to high gravity molasses.
Erlenmeyer flask (100 ml) was filled with 10 ml of the molasses dilution, which was
then autoclaved and incubated at 30ºC overnight for sterility check. After 24 h, a loop
full culture was collected from previously preserved petri plates and transferred into
these flasks which were then incubated in shaker incubator at 30ºC with 100 rpm for
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24 h. After completion of incubation time, 20 ml of the yeast culture was transferred
into Erlenmeyer flask (500 ml) containing 250 ml of sterilized molasses dilution
(1.050 sp. grv; 9% sugar conc.) and again incubated at 30ºC for 24 h in shaker
incubator with 100 rpm for inoculum development. This stepwise increase in
molasses gravity was adopted to acclimatize yeast cells to high osmotic environment.
Same procedure was followed for all the yeast strains and repeated for all the
experiments on molasses.
3.3.4. Osmotic Tolerance
Sugarcane molasses was diluted with distilled water to prepare various concentrations
between 18-58% (w/v) and specific gravity values in range of 1.050-1.150, with the
help of gravity hydrometer. The sugar concentration was estimated between 9-29%
(w/v) by dividing total sugar added with dilution factor. These set of dilutions were
prepared for all of the selected stains and inoculated by 24 h old inoculum of each
strain and incubated at 30ºC for 72 h. After completion of reaction, all the dilutions
were distilled to determine ethanol concentration with the help of high performance
liquid chromatography (HPLC) and fermentation efficiency of all the strains at
different sugar concentration was also calculated by the formula:
Fermentation efficiency % = Actual Ethanol yield × 100
Theoretical Yield
Where, Theoretical Yield (v/v) = Sugar concentration × 0.64
On the basis of actual ethanol yield and fermentation efficiency, most osmotic tolerant
commercial strains were selected and compared with best self-isolated indigenous
strain (MZ-4) under optimized physicochemical conditions for enhanced production
of bioethanol from molasses.
3.3.5. Effect of Physicochemical and Nutritional Parameters
Different physicochemical parameters i.e. pH, temperature, inoculum size and age
were optimized for best selected yeast strains to get maximum ethanol production
from sugarcane molasses. Effect of different nitrogen sources and chelating agents on
these strains for enhanced ethanol production was also determined.
(a) Effect of pH
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To study the optimized pH value of yeast strains, 500 ml molasses dilution having
optimized sugar concentration was taken in Erlenmeyer flasks (3 L capacity) and their
pH was adjusted in range of 3.0-6.0 with the help of 5N H2SO4 and 5N NaOH. All the
flasks were inoculated with 5% (v/v) of 24 h old yeast inoculum and incubated at
30ºC for 72 h. Same procedure was repeated for all the yeast strains selected from
previous experiments.
(b) Effect of Temperature
To determine the best temperature for all selected strains, 500 ml molasses dilution
which contained optimized sugar concentration in 3L Erlenmeyer flask was adjusted
with previously optimized pH with respect to the specific inoculating strain. All flasks
were inoculated with 5% (v/v) of 24 h old inoculum of that strain and incubated at
different temperatures ranges 27-39ºC for 72 h. Same experiment was repeated for all
selected strains.
(c) Effect of Inoculum size
Experiment was set on the basis of all previously optimized parameters and varying
quantity of inoculum was added in range of 2.5-12.5% (v/v) to determine the best
inoculum size of each selected strain. Yeast cells were stained with 0.01% (w/v)
methylene blue and live yeast cell count in 24 h old inoculum was determined by
haemocytometer. The inocula of all selected strains were centrifuged at 2500 rpm for
5 min and the supernatant was discarded. Sterilized saline solution [0.9% (w/v) NaCl]
was added to yeast cell pellet to dilute the cells concentration up to 300x106 per
milliliter counts. Ethanol content was determined in fermentation media after 72 h of
incubation at the optimized temperature of each strain.
(d) Effect of Inoculum Age
To determine the effect of inoculum age, selected strains were cultured for 12, 24, 36
and 48 h. Then the inocula were centrifuged and diluted with saline to adjust cell
count up to 300x106 per milliliter. Already optimized size of inocula was used to
carry out fermentation process. All conditions were set to optimized values and
incubation was carried out for 72 h.
(d) Effect of Nitrogen Sources
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Nitrogen plays a significant role to enhance ethanol yield, due to which various
nitrogen sources were studied to determine their effect in enhanced ethanol
production. Urea, ammonium sulfate, ammonium nitrate, di-ammonium phosphate,
and ammonium chloride in various concentration ranges from 0.05-0.15% (w/v) were
added in molasses dilution at optimized sugar concentration, with adjusted optimized
pH value and inoculated with 5% (v/v) of 24 h old inoculum. The fermentation media
was then incubated at their optimum temperature for 72 h. Same experiment was
repeated for all selected strains.
(f) Effect of Chelating Agents
Chelating agents such as EDTA (Ethylenediamine tetraacetic acid), potassium
ferrocyanide, and sodium potassium tartrate were studied by adding them in various
concentrations ranges from 0.0025-0.32% (w/v) in to molasses dilutions. Effect of
chelating agent on fermentation by selected yeast strains was studied at their
optimized molasses concentration and pH by inoculating 5% (v/v) of 24 h old yeast
culture. The fermentation process was carried out by providing incubation at already
determined optimized temperature for 72 h. Same procedure was followed for all
strains.
After the completion of all the experiments, ethanol content was determined in
fermentation media with HPLC after distillation. The fermentation efficiencies of all
the selected strains were again calculated under optimized physicochemical
parameter.
3.4. FED BATCH FERMENTATION
The most ethanol tolerant comercial strain i.e. Lalvin EC-1118 (18% (v/v) ethanol tolerance)
was selected and compared with newly isolated strain MZ-4 (15% (v/v) ethanol tolerance),
and their ethanol producing potential in molasses was determined by fed-batch fermentation.
During fed-batch fermentation molasses was fed in intervals to reduce the osmotic stress
faced by fermenting microbes due to high sugar concentration in batch fermenter. For this
reason different molasses dilutions were prepared for each strain, having specific gravity
ranges from 1.080-1.140, with the help of gravity hydrometer. Four sets of flask for each
molasses dilution were prepared and they were assigned label 12, 24, 36 and 48 h. Molasses
dilutions (500 ml) were added to 5 L flask along with optimized nutrient addition and
inoculum and pH was adjusted to optimized value. All the flasks were incubated at the
already optimized temperature of the inoculated strain. All the four sets were fed after every
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12, 24, 36 and 48 h, respectively. The drop in specific gravity was noted after their assigned
time and more pure molasses was added into it to raise the specific gravity equals to initial
condition. Same procedure was repeated until no reduction in specific gravity was noted after
the assigned time interval. Fermentation media was distilled when the process was completed
and ethanol was determined by HPLC. Same procedure was repeated for all the three strain.
Fermentation efficiency of each strain at various specific gravity with different feeding rate
was also calculated.
3.5. ANALYTICAL METHODS
3.5.1. Lane and Eynon Method
Lane and Eynon titration method was used to determine reducing sugars in any
substance. Fehling’s solution A was prepared by dissolving 3.463 g of copper
sulphate (CuSO4.5H2O) in 50 ml water and filtered through Whatman filter paper.
Fehling’s solution B was prepared by adding 17.3 g of sodium potassium tartrate
(KNaC4H4O6.H2O) in 30 ml of water along with the solution of NaOH (prepared by
adding 5 g of NaOH in 5 g of water). The solution was allowed to cool and its volume
was increased up to 50 ml by adding distilled water. Methylene blue indicator (1%
w/v) was prepared by dissolving 1 g of indicator in 100 ml of water.
Standardization of Fehling’s Solution
Fehling’s solution A (12.5 ml) was mixed with Fehling’s solution B (12.5 ml) in 250
ml conical flask and 25 ml of water was added into same flask. Burette was filled with
standard glucose solution that was prepared by adding 1.25 g of glucose in 250 ml of
water. The Fehling’s solution was titrated against glucose solution at boiling
temperature and 23.5 ml of glucose solution was added from burette. Methylene blue
solution was added into Fehling’s solution and again few drops of glucose solution
were added from burette until the blue color completely disappeared. Exactly 24.1 ml
of glucose solution was used to standardize titration which showed the Fehling’s
solution is quite appropriate for sugar determination. The Fehling’s solution was then
used to determine the amount of total sugar by using factor: 25 mL of Fehling’s
solution = 0.1205 g of RS (reducing sugar)
3.5.2. Dinitrosalicylic acid (DNS) Method
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Reducing sugar can be determined by DNS method proposed by Miller (1959). The
DNS reagent was prepared by mixing 10 g of dinitrosalicylic acid and 10 g of NaOH
in 500 ml of water. In another flask, 200 g of potassium sodium tartrate was dissolved
in 200 ml water and 2 g of melted phenol was added into it. Both solutions were
mixed and volume was increased up to 1 L. A stock containing 0.1 g of glucose in
100 ml of water was prepared and glucose solutions of different concentrations were
prepared. In 1 ml of each dilution, 3 ml of DNS reagent was added and heated at 90ºC
for 5 min. Then all tubes were cooled in ice cold water then 200µl from each solution
was diluted to 2.5 ml of water and optical density was measured at 540nm to
formulate calibration curve (Appendix C.1). Sugar concentration of molasses sample
was determined by using linear regression equation obtained by standard curve i.e.
y = bx + a
Where the b represents slope, and a represents intercept of the line
3.5.3. Estimation of Alcohol Contents
3.5.3.1. Distillation Method
After completion of fermentation process, a known volume of fermentation media
(i.e. 100 ml) was distilled at 78ºC. The ethanol was collected at receiving flask. The
ethanol content in collected fraction was determined with the help of HPLC and the
concentration of ethanol in fermentation medium was determined by the formula:
C1V1= C2V2
Where C1 and V1 were the concentration and volume of fermentation media heated in
distillation flask, whereas C2 is concentration of the ethanol in distillate that was
determined by HPLC, and V2 is volume of the distillated collected in receiving flask.
High Performance Liquid Chromatography (HPLC)
Ethanol content in collected distillate was determined by HPLC (Waters 1525) with
IC-PAKTM
Ion Exclusion column [50 Aº 7µM (300 × 7.8mm)] and RI detector
(Waters 2410) by using 0.5 mM H2SO4 as the mobile phase and injection volume of
20 μl at flow rate of 0.5ml/min. Ethanol calibration curve was developed by using
various concentration of ethanol i.e. 10, 20, 30, 40 and 50% (Appendix C.2). All
samples collected after distillations were compared with this HPLC calibration curve
to determine the exact concentration of ethanol. All the standards and samples were
filtered through 0.2 μm cellulose-acetate filter paper before HPLC analysis.
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3.5.4. Yeast Cell Counting: (Mills, 1941)
Live yeast cells were counted with the help of haemocytometer already cleaned with
70% ethanol. For this purpose, 1ml of 24 h old inoculum was diluted in 10 to 100 ml
(depending upon the concentration of cells) distilled water. After dilution 0.5 ml of
sample was mixed with 0.5ml of 0.01% (w/v) methylene blue. A micropipette was
then used to transfer 10 µl of sample into haemocytomter and allowed the cells to
settle down for 1 min. The yeast cells were then examined under microscope with
100x magnification. All the dead cells were stained blue while the live cells were
colorless. Cells in four large corners were counted while neglecting cells touching left
and lower margins. The live cell count was determined by following formula:
Live yeast cell counts (cell/ml) = (live yeast count / No of squares) x 104
PART-B: ENHANCED PRODUCTION OF BIOETHANOL FROM
SUGARCANE BAGASSE
3.6. BIOMASS PREPARATION
3.6.1. Raw Material
Sugarcane bagasse was supplied by Green Energy Inc. Vonore, TN, USA. Bagasse (5-8 cm
size) was air-dried for two-three days. It was placed inside plastic bags and stored at 4ºC for
further use.
3.6.2. Drying and Milling
Bagasse was dried for two-three days until its moisture content became less than 10%. The
dried bagasse was milled in Thomas Model 4 Wiley® Mill fitted with 40 mesh screen to get
final particle size of about 0.45 mm.
3.6.3. Soxhlet Extraction
Removal of extractives present in lignocellulosic biomass is one of the important
steps while performing structural analysis, as these extractives can create problems by
interfering with other chemicals and reduce the precision of particular analysis. After
size reduction, sugarcane bagasse was extracted by placing the biomass into thimble
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of soxhlet extractor. The upper part of thimble was connected with condenser while
its lower part was fixed with receiving flask containing dichloromethane (1:10 mass
to liquid ratio). Biomass was refluxed with dichloromethane for 24 hours at 4-5
extractions per hour according to Tappi method T204 cm-07. After extraction,
biomass was removed from extraction thimble, and solvent was evaporated near to
dryness in the chemical fume hood.
3.7. PRETREATMENT STRATEGIES
3.7.1. Autohydrolysis of Sugarcane Bagasse
Sugarcane bagasse was treated with hot water in 4560 mini-parr pressure reactor.
Pretreatment conditions were selected on the basis of previously reported data.
Batalha et al. (2015) reported 190ºC±5 for 10 min and Peterson et al. (2009)
suggested 205ºC±5 for 6 min were comparatively better conditions for maximum
sugar recovery from lignocellulosic biomass. To compare the effectiveness of these
two conditions suggested in previous studies, 5 g of sugarcane bagasse was mixed
with 100 ml of water (20:1 liquid to solid ratio) and heated under these conditions in
mini Parr reactor separately. Untreated bagasse was considered as control.
Temperature increase rate at both conditions was determined as 4-5ºC per minute.
Pressure was noted as 14 Barr and 18 Barr when reactor heated at 190ºC and 205ºC,
respectively. After completion of pretreatment, reactor was quenched in ice cool
water for rapid cooling.
Filtration and Solid Recovery after Autohydrolysis
After autohydrolysis each set of pretreated bagasse was filtered through VWR Grade
417 filter paper with the help of vacuum filtration technique. Solid content was
collected in filter paper and kept inside fume hood for complete drying. Biomass after
autohydrolysis was not oven dried to prevent reduction in pore size and damage of
cellulose structure (Zhang et al., 2012).
3.7.2. Ionic liquid (IL) Pretreatment
Ionic liquid (1-butyl-3-methylimidazolium acetate) was added in sugarcane bagasse to
set liquid to solid ratio of 20:1 (5% w/v bagasse solution) and heated up to 110 C 5
for 30 min. The impeller was adjusted at speed of 100 rpm and reactor was heated to
specific temperature (at ~ 4-5 C/minute). After completion of pretreatment time the
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reactor was dipped into ice bath (~5 minutes) for rapid cooling. Untreated bagasse and
water treated bagasse were used as control to compare the effectiveness of ionic liquid
pretreatment. In water-treated bagasse sample, water was added instead of ionic liquid
and heated at same conditions i.e. 110ºC for 30 min. All experiments were conducted
in duplicates.
Filtration and Solid Recovery after IL pretreatment
Post pretreatment, deionized water was added into the IL and biomass solution at a
ratio of 5:1 (water: IL) to recover the biomass. Deionized water was added to it at
room temperature and stirred vigorously to enable biomass regeneration. The solids
were washed repeatedly with deionized water to remove any remaining IL from the
samples until the washed solution appeared colorless and solids were collected. The
ionic liquid/water mixture and biomass were separated by vacuum filtration through
VWR Grade 417 filter paper. Then recovered biomass was dried for two days before
further experiments (Zhang et al., 2012).
3.7.3. Severity Factor
In order to compare the efficacy of various pretreatment techniques, the
severity factor of all the pretreatments were determined by using the
equation:
SF = log (t x exp((T − Tref)/14.75))
In the above equation, t is the treatment time in min, T is the treatment temperature,
Tref is the reference temperature (i.e., 100°C) and 14.75 is an empirically determined
constant (Soudham et al., 2015)
3.8. COMPOSITIONAL ANALYSIS OF SUGARCANE BAGASSE
In order to monitor changes in biomass composition as a result of pretreatments and to
calculate the sugar conversion from enzymatic hydrolysis, carbohydrate and lignin analysis
were carried out based on methods described in NREL/TP-510-42618.
3.8.1. Lignin Determination
(a) Acid Insoluble lignin (Klason lignin)
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Acid Insoluble lignin (Klason lignin) of the control and pretreated samples were
determined by Tappi T-249 method. An oven dried sugarcane bagasse sample (0.175
g) was taken in a digestion tube and 1.5 ml of 72% (w/v) H2SO4 was added into it.
The sample was stirred with glass rod and after covering the cap with Parafilm,
digestion tube was placed in water bath at 30ºC. Glass rod was left in digestion tube to
stir it occasionally during primary hydrolysis. After one hour the sample was removed
from the water bath and 42 ml of distilled water was added into it for secondary
hydrolysis step during which bagasse was heated in 3% (w/v) H2SO4. Disposable
pipette was used to clean the glass rod during addition of water. The digestion tube
was loosely caped and was autoclaved at 121ºC for one hour. After autoclave, when
digestion tubes were cooled down, the solution inside tube was filtered through G8
(glass fiber filter) and more distilled water was added to make the volume of filtrate
up to 50 ml. A part of filtrate was used to determine acid soluble lignin and the rest
was stored in refrigerator for carbohydrate analysis. Glass fiber filter was prepared by
placing it in crucibles and washed by filtering distilled water through it; and then
crucible was left in an oven at 105ºC for 2 h. After drying, the crucible was removed
from oven and placed in desiccator for 20 min and weighed. After filtration of sample
through G8 filters, the remaining residue on filters were placed in oven at 105ºC and
left overnight. Next day, the crucibles were again cooled inside desiccator for 20 min
and weighed. The residue collected on fiber divided by the dry weight of the bagasse
(i.e. 0.175g) showed the weight of klason lignin per gram of substrate. Same
procedure was repeated in duplicates for all treated and untreated samples.
(b) Acid soluble Lignin (ASL)
Acid soluble lignin was analyzed in aliquots of filtrates by UV-Vis
Spectrophotometer within six hours after secondary hydrolysis. The absorbance was
noted at 240 nm by using 1cm light path Quartz cells and deionized water was used as
blank. The sample was diluted 4 times. The total insoluble lignin was determined by
the formula:
ASL% = (UVabs x Total volume of filtrate x Dilution factor ) x 100
є x ODWsample x Path length
Where,
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UVabs = average UV-Vis absorbance for the sample at 240nm
Volume hydrolysis liquor = volume of filtrate, 0.050 L
Dilution = (Volume of sample + Volume of diluting solvent)/Volume sample
ε = Absorptivity of biomass at 240nm = 24 (L/g-cm)
ODWsample = weight of sample in grams
Path length= path length of UV-Vis cell in cm
3.8.2. Carbohydrate Analysis
Sugar analysis after wet chemistry was done to determine compositional analysis of
pretreated and untreated biomass. All treated and untreated samples were analyzed for
glucan, xylan, arabinan and mannan content with the help of HPLC.
3.9. STRUCTURAL ANALYSIS OF SUGARCANE BAGASSE
3.9.1. Fourier Transform Infrared Spectroscopy (FTIR)
To investigate and estimate chemical changes in the sugarcane bagasse samples after each
pretreatment, a Perkin Elmer Spectrum 100 FTIR spectrometer equipped with an Attenuated
Total Reflectance (ATR) sampling accessory (Perkin-Elmer Inc., Wellesley, MA, United
States) was used. Samples (20 mg) were pressed uniformly against the crystal surface via a
spring-anvil, and spectra were obtained after 32 scans accumulation from 4,000 to 600 cm−1
at
4 cm−1
resolution. The ATR correction, which was performed using the formula AATRcorr
=
AATR
(k/k0) and setting the correction factor k0 to 1000 cm-1
(M. Milosevic, Internal
Reflection and ATR Spectroscopy (John Wiley & Sons, 2012)), and the baseline correction
were carried out by the Perkin-Elmer Spectrum software 8 (Perkin-Elmer Inc., Norwalk, CT,
United States). All FTIR graphs represented wavenumber in cm-1
on the x-axis and
absorbance on the y-axis (Sun et al., 2015)
.
3.9.2. X-ray Powder Diffraction (XRD)
Crystallinity index (CrI) of untreated, autohydrolysed and IL treated sugarcane
bagasse material was analyzed by X-ray diffractometer (PANalytical 3040/60 X'pert
PRO, Netherlands) with CuKα radiation source (k = 0.1505nm). Patterns were
collected from 5 to 40 (2θ) with scan step of 0.01 , while the operating voltage and
current were 40kV and 30mA, respectively. The crystallinity index (CrI) was defined
using the equation:
CrI= (I002-Iam)/I002
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Where I002 is the maximum intensity of crystalline peak at 2θ (22 ), whereas Iam is the
scattered intensity due to the amorphous portion evaluated as the minimum intensity
between the main (I002) and secondary peaks (I101) (Qiu et al., 2012)
3.10. ENZYMATIC SACCHARIFICATION
A combination of two commercially available enzymes cellulase (Celluclast® 1.5L,
Sigma Aldrich) and β-glucosidase from almond (CAS No: 9001223; Sigma Aldrich)
was used for the hydrolysis of untreated, water-treated and ionic liquid-treated energy
cane bagasse. The activity of cellulase was determined as filter paper assay unit (FPU)
by LAP (Laboratory Analytical Procedures) TP-510-42628 documented by NREL.
3.10.1. Enzyme Loading Optimization
(a) For Autohydrolysed Samples
Cellulase and β-glucosidase was added in different ratios (5FPU:10IU; 10FPU:20IU,
20FPU:40IU) to determine the exact loading amount for maximum sugar release from
pretreated biomass. In structural and compositional analysis, there was no wide
difference observed in cellulose crystallinity and quantity, among samples
autohydrolysed at 190ºC and 205ºC. Thus the optimization was carried out only by
using bagasse pretreated at 190ºC for 10 min. Reducing sugar released was
determined by DNS method (Miller, 1959) after every 24 h until the process
completed.
(b) For Ionic liquid Treated Samples
In order to determine the maximum loading required for the saccharification of IL
pretreated bagasse, cellulases and β-glucosidases were added in different ratios i.e.
5FPU:10IU; 10FPU:20IU, 20FPU:40IU; 40FPU:80IU. The best loading amount
determined for IL pretreatment was added for further enzymatic hydrolysis of IL-
pretreated biomass.
3.10.2. Enzymatic Hydrolysis
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All pretreated and untreated bagasse samples were subjected to enzymatic hydrolysis
by adding 1g substrate in 100 ml (1% w/v) of 50mM sodium citrated buffer (pH 4.8).
The optimized dosage of cellulases and β-glucosidases was chosen for hydrolytic
process. The process was carried in rotary incubator with a shaking speed of 150 rpm
at 50ºC for 72 h. Aliquots (500 µl) were collected at 3, 6, 12, 24, 48 and 72 h. Each
aliquot was sealed and incubated for 5 min at boiling water to denature the cellulases
(Zhang et al., 2012). The aliquots were filtered through 0.20 µm Nylon syringe filter
(Millipore, Billerica, MA) before high performance liquid chromatography (HPLC)
analysis. All experiments were performed in duplicates.
(a) Cellulose Digestibility Percentage
Percentage digestibility of cellulose was calculated as:
Percentage digestibility= (gram cellulose digested/ gram cellulose added) x100
(b) Xylan Digestibility Percentage
Percentage digestibility of xylan was calculated as:
Percentage digestibility= (gram xylan digested/ gram xylan added) x100
3.11. FERMENTATION
Three strains of S. cerevisiae and one strain of P. stipites (ATCC 58785) were used to
determine an efficient strain for enhanced ethanol production in case of each
pretreatment study. A newly isolated strain of S. cerevisiae MZ-4 and two commercial
strains of S. cerevisiae i.e. Lalvin EC-1118 and Uvaferm-43 were used for
fermentation process. After enzymatic saccharification, liquid part of all pretreated
samples were subsequently autoclaved and allowed to cool before inoculation, and all
the four strains were inoculated separately with inoculum size of 5% v/v (containing
300 x 106
living cells/ml). Ethanol content was measured from fermentation media
after every 12 h to determine maximum ethanol concentration produced per gram of
treated sample (Boopathy and Dawson, 2008; Singhania et al., 2014).
3.12. ANALYTICAL METHODS
Carbohydrate Analysis of Biomass by HPLC
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HPLC analysis was done to quantify the sugars released during enzyme hydrolysis,
and to determine the compositional analysis of bagasse. An HPLC system (Perkin
Elmer Flexar HPLC, Perkin Elmer, Shelton, CT) with Bio-Rad Aminex HPX-87P
column and refractive index detector was used (Appendix C.3-C.6). The temperature
for the column was set at 85ºC and H2O was used as the mobile phase with a flow rate
of 0.25 ml/min. The Chromera® Chromatography Data Systems (CDS) software was
used for the analysis and interpretation.
Determination of Cellulase Activity (Filter Paper Assay)
In order to measure the cellulase activity, 50 mg Whatman No. 1 filter paper strip (1.0
x6.0 cm) was rolled and placed into enzyme assay tubes. Sodium citrate buffer
(50mM; pH 4.8) of the amount 1.0 ml was added into these tubes and were
equilibrated at 50ºC. Different dilutions of enzymes were prepared in citrate buffer
and 0.5ml of enzyme dilution was added into enzyme assay tube. All the tubes were
incubated at 50ºC for 60 min. When reaction was completed, all the tubes were
removed from water bath and reaction was stopped by adding 3.0 ml of DNS in each
tube. Sodium citrate buffer (1.5 ml) was used as blank, whereas, a substrate control
(1.5 mL citrate buffer + filter-paper strip) and an enzyme control (i.e. 1.0 mL citrate
buffer + 0.5 mL enzyme dilution) were used as process controls. For each enzyme
dilution separate enzyme control was prepared. All blank and controls were also
incubated at 50ºC for 60 min and reaction was stopped by adding 3.0 ml DNS. All the
tubes were covered properly to prevent evaporation and boiled for 5 min in water
bath. The tubes were then transferred to ice cold water to terminate the reaction.
When all the pulp settled down, 0.2 ml of sample from each tube was diluted to 2.5 ml
of water and absorbance was determined by UV-vis spectrophotometry at 540 nm.
The readings were compared with glucose standard curve which was prepared by
adding DNS in various concentrations of glucose-buffer solutions. The enzyme
dilution which released 2mg/ml of the glucose was determined by linear regression
formula obtained by standard curve of glucose. The filter paper assay unit was
determined by formula:
Filter paper activity (units /ml) = [0.37] / [enzyme] releasing 2mg/ml glucose
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Where [enzyme] represents the proportion of original enzyme solution present in the
directly tested enzyme dilution (that dilution of which 0.5 mL is added to the assay
mixture)
3.13. STATISTICAL ANALYSIS
The mean and standard deviation was determined for all experiments. One way
Anova was used to determine significance across groups, and post-hoc tukey tests
were used for pairwise comparison to determine significance between groups, carried
out by IBM SPSS software 23. P-values of less than 0.05 were considered as
significantly different. Graph preparation and standard deviation calculations were
performed in Microsoft Excel, 2010.
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Chapter 4
Results
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PART A: ENHANCED PRODUCTION OF BIOETHANOL FROM
SUGARCANE MOLASSES
For the enhanced production of bioethanol from sugarcane molasses, this part of
research was further divided into four main sections. In first section, the chemical
composition of sugarcane molasses, which was obtained from Murree Brewery,
Rawalpindi, Pakistan, was determined. In the next section, ethanol tolerant yeast
strain was isolated from fruits and identified at molecular level. In third section, most
tolerant self-isolated strain was compared with the already available commercial
strains during optimization process. In last section, an attempt was made to enhance
the production of ethanol by fed-batch fermentation process.
4.1. PHYSICOCHEMICAL PROPERTIES OF MOLASSES
The physicochemical properties of molasses were determined by conventional
methods. The results of various experiments to determine physicochemical properties
of molasses were illustrated in Table. 4.1. The dissolved solid particle of molasses
was determined with the help of brix refractometer. It was an important parameter to
be studied before start of the work because most of the ethanol industries diluted their
molasses according to its ºbrix values. The ºbrix of molasses during current research
was noted as 79.0 brix. Specific gravity is another important parameter to determine
before the start of new experiments. The specific gravity noted with the help of
gravity hydrometer was 1.4. The sugar concentration of molasses was determined by
various conventional methods. As molasses contained both reducing as well as non-
reducing sugars, therefore, a modified Lane and Eynon method was first used to
determine its total sugar concentration. During this experiment, molasses was heated
with the addition of HCl and all the non-reducing disaccharides present in molasses
were converted into monomeric reducing sugars, which were then detected by
Fehling’s solution and calculated as 49% (w/w). This value showed the amount of
both reducing as well as inverted sugars. The DNS method was used to determine the
reducing sugars in non-treated molasses, which was noted as 15% (w/w) that
excluded the values of non-reducing sugar. The value of non reducing sugar was
determined as 32.3% (w/w). The ability of yeast to convert all the sugars (reducing
and non-reducing) into ethanol made it important to determine the concentration of
total sugars present in molasses.
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Table 4.1: Physicochemical Properties of Molasses
No Components Amount
1. Brix 79.0 °Bx ±1.0
2. Specific Gravity 1.4 ± 0.05
3. Reducing Sugar (w/v) 15.0 % ±0.50
4. Non Reducing Sugar (w/v) 32.3% ± 1.0
5. Total Sugar (w/v) 49.0% ±1.0
4.2. ISOLATION, SCREENING AND CHARACTERIZATION OF
INDIGENOUS YEAST STRAINS
4.2.1. Isolation and Screening
Variety of sources were selected and processed for isolation of yeast. The number of
strains isolated from grapes and strawberry were 22 and 3, respectively, whereas no
yeast strain could be isolated from carrot and soil samples. All yeast strains were then
subjected to grow in YPD broth medium containing 10% and 15% ethanol.
The results showed that five of the isolated strains i.e. MZ-1, MZ-4, MZ-12, MZ-18
and MZ-22 were able to grow in 10% ethanol containing YPD broth that represented
the hight tolerance of these strains against the ethanol concentration present in that
medium as compared to the rest of the strains (Table. 4.2.a). Only one strain MZ-4
exhibited comparatively better growth and tolerance upto 15% ethanol concentration
in YPD broth (4.2.b). Thus, the strain MZ-4 was selected for further studies on the
basis of its high ethanol tolerance so that it could be compared with some very good
ethanol tolerant commercially available strains.
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Table 4.2(a): Screening of Isolated Yeast Strains against 10% Ethanol Tolerance
Yeast strain Optical Density at 600nm after every 24 hour
0 h 24 h 48 h
MZ-1 1.502 2.327 2.500
MZ-2 0.53 0.524 0.510
MZ-3 0.345 0.524 0.590
MZ-4 0.965 2.001 2.221
MZ-5 0.652 0.599 0.59
MZ-6 1.986 2.060 1.856
MZ-7 1.521 1.321 1.32
MZ-8 0.53 0.521 0.501
MZ-9 0.963 1.546 2.570
MZ-10 0.632 0.624 0.312
MZ-11 1.011 0.915 0.832
MZ-12 0.937 1.815 1.945
MZ-13 1.021 0.950 0.810
MZ-14 1.342 1.321 1.212
MZ-15 0.702 0.654 0.525
MZ-16 2.012 1.985 1.895
MZ-17 2.222 2.170 2.135
MZ-18 0.399 0.416 0.723
MZ-19 0.77 0.759 0.750
MZ-20 1.551 1.542 1.540
MZ-21 2.19 2.195 2.001
MZ-22 0.852 1.416 1.850
MZ-23 0.645 0.652 0.552
MZ-24 1..511 1.501 1.382
MZ-25 1.1 1.918 1.824
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Table 4.2(b): Screening of Isolated Yeast Strains against 15% Ethanol Tolerance
Yeast strain Optical Density at 600nm after every 24 hour
0 h 24 h 48 h
MZ-1 0.421 0.316 0.220
MZ-2 0.366 0.304 0.310
MZ-3 0.459 0.455 0.420
MZ-4 0.502 0.669 0.920
MZ-5 0.54 0.504 0.501
MZ-6 0.499 0.459 0.439
MZ-7 0.51 0.499 0.503
MZ-8 0.503 0.507 0.506
MZ-9 0.507 0.513 0.486
MZ-10 0.52 0.519 0.515
MZ-11 0.401 0.414 0.400
MZ-12 0.313 0.303 0.302
MZ-13 0.515 0.523 0.521
MZ-14 0.45 0.456 0.411
MZ-15 0.32 0.315 0.301
MZ-16 0.315 0.321 0.312
MZ-17 0.59 0.600 0.508
MZ-18 310 0.299 0.298
MZ-19 0.344 0.358 0.350
MZ-20 0.5 0.507 0.500
MZ-21 0.46 0.458 0.369
MZ-22 0.453 0456 0.432
MZ-23 0.415 0.421 0.422
MZ-24 0.65 0.621 0.525
MZ-25 0.666 0.655 0.620
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4.2.2. Identification of Selected Yeasts
The strain MZ-4 was selected and identified through microscopic examination and
morphology on WLN agar plate. Buddings were clearly observed on microscopic
examination that considered as one of the major characteristics of yeast strain. Strain
MZ-4 has dark green, large, oval and elevated colonies on WLN medium, that showed
its resemblance to Saccharomyces, which was further confirmed by molecular
identification.
18S rRNA nucleotide sequence obtained from Macrogen Incorporation, Seoul, Korea,
was further analyzed by using NCBI blast technique. Strain MZ-4 showed 100%
similarity with Saccharomyces cerevisiae type strain S288c. The sequence was
submitted to gene bank and an accession number i.e. KP970869 was assigned. The
evolutionary history of strain MZ-4 was represented by formulating the phylogenetic
tree using neighbor-joining method with the help of Mega-6 software (Fig.4.1)
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Fig.4.1: Phylogenetic tree of isolated Saccharomyces cerevisiae strain MZ-4
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4.3. SELECTION OF BEST COMMERCIAL YEAST STRAIN TO COMPARE
WITH BEST INDIGENOUS YEAST STRAIN MZ-4
4.3.1. Selection of Commercial Strains
Four commercial strains i.e. Rossmoor, Saf-Gold, Uvaferm-43 and Lalvin EC-1118
were selected and their ethanol tolerance from already published data was found as 6,
12, 18 and 18% (v/v) respectively (Bechem et al., 2007; Schmidt et al., 2011; Sultana
et al., 2013). The strains exhibited comparatively more ethanol and osmotic tolerance
along with better fermentation efficiency was selected to compare with newly isolated
indigenous strain MZ-4.
4.3.2. Osmotic Tolerance
Osmotic tolerance of all the strains was determined by carrying out fermentation of
different molasses dilutions and quantifying the ethanol yield with the help of HPLC
(Table 4.3). It was observed that the ethanol production for all the strains was
increased with the increase in molasses concentration due to more sugar availability;
however, after certain concentration of molasses, the ethanol production was reduced
because of their osmotic intolerance at high sugar concentrations. It was observed that
the commercial strains i.e. Rossmoor and Saf-instant, was producing 6.5 and 7.5%
(v/v) of ethanol when 15 and 17% (w/v) of sugar was present in the fermentation
medium, respectively. However, Uvaferm-43, Lalvin EC-118 and MZ-4 were tolerant
to 25% (w/v) sugar and they produced maximum of 9.3, 9.6 and 10.1% (v/v) of
ethanol, respectively.
The fermentation efficiency of the process at different sugar concentration was also
calculated. It was determined that the fermentation efficiency of the process decreased
with increase in sugar concentration. The Rossmoor strain showed fermentation
efficiency of 72.6% in presence of 9% (w/v) sugar concentration and yielded 4.1%
ethanol. The increase in sugar concentration up to 15% (w/v) enhanced ethanol yield
up to 6.5% (v/v), but the fermentation efficiency reduced to 67.3%. In case of Saf-
instant yeast, the maximum fermentation efficiency of 75.6% was noted with 4.2% of
ethanol yield when 9% (w/v) sugar was present in molasses. The maximum amount of
ethanol produced by this strain was 7.5% (v/v) with 17% (w/v) sugar concentration;
however, the fermentation efficiency was reduced to 57.5%. Uvaferm-43, Lalvin EC-
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1118 and MZ-4 strains showed 85.1, 85.1 and 83.3% fermentation efficiency with the
production of 4.8, 4.8 and 4.7 % (v/v) of ethanol respectively. The increase in sugar
concentration up to 25% (w/v) enhanced their ethanol yield up to 9.3, 9.6, 10.1%
(v/v), but the fermentation efficiency was reduced to 58.1, 60.0 and 63.1%
respectively. On the basis of these results, the commercial strain Lalvin EC-1118 was
selected for further studies to compare with self-isolated MZ-4 strain, as both of these
strains were tolerant to 25% (w/v) sugar concentration and showed comparatively
better ethanol yield and fermentation efficiency as compared to other strains.
4.3.3. Ethanol Quantification by HPLC
The HPLC chromatogram for ethanol showed its peak with retention time of 14.6 min
(Fig 4.2). The calibration curve for ethanol was formulated by plotting the area of
peak (at 14.6 min) against different concentration of ethanol (Appendix C2). The
ethanol yield (Table 4.3) was determined by distillation of fermentation media after
completion of process, and distillate was run through HPLC to compare with
calibration curve.
Table.4.3: Enhanced production of bioethanol by various yeast strains using different concentration of sugar.
Sugar
(%)
Actual Ethanol yield % (v/v) Fermentation Efficiency (%)
Rossmmor SAF-
instant
Uvaferm
-43
Lalvin
EC-
1118
MZ-4 Ross
moor
SAF-
Instant
Uvaferm-
43
Lalvin
EC-118 MZ-4
9 4.1±0.08 4.2±0.04 4.8±0.08 4.8±0.02 4.7±0.16 72.6 75.6 85.1 85.1 83.3
11 4.8±0.12 5.3±0.08 5.7±0.12 6±0.12 5.7±0.04 68.5 75.2 81.9 85.2 81.91
13 5.5±0.04 6.2±0.16 6.9±0.08 6.4±0.16 5.9±0.08 66.4 74.4 82.8 76.8 71.2
15 6.5±0.12 7.1±0.08 7.2±0.16 7.5±0.02 6.4±0.14 67.3 73.9 75.00 78.1 67.3
17 6.4±0.12 7.5±0.04 7.8±0.08 7.8±0.16 7.2±0.08 59.1 69.2 71.6 72.3 66.1
19 6.1±0.08 7.0±0.08 8.1±0.08 8.1±0.08 7.8±0.02 50.1 57.8 66.6 67.1 64.1
21 5.4±0.04 6.7±0.04 8.5±0.08 8.5±0.04 8.4±0.04 40.4 50.3 63.2 63.7 62.9
23 4.3±0.08 6.1±0.08 8.7±0.08 9.2±0.14 9.2±0.04 29.2 41.4 59.1 62.7 62.9
25 3.6±0.04 5.6±0.16 9.3±0.08 9.6±0.16 10.1±0.12 22.9 35.0 58.1 60 63.1
27 3.4±0.08 5.4±0.08 8.5±0.12 8.6±0.02 8.1±0.14 19.6 31.2 49.5 49.9 46.8
29 2.4±0.08 4.7±0.12 7.7±0.08 8±0..18 7.5±0.02 12.9 25.6 41.4 43.1 40.4
PhD Thesis
Enhanced production of biofuel from sugar industry waste 72
Fig.4.2: HPLC chromatogram for ethanol detection
PhD Thesis
Enhanced production of biofuel from sugar industry waste 73
4.3.4. Effect of Physicochemical and Nutritional Parameters
(a) Effect of pH
To determine the effect of pH on each of the selected strains, the production of
ethanol was studied by adjusting the pH in range of 3-6 (Fig.4.3, Appendix D1). It
was observed during the optimization study that the production of ethanol decreased
under either more acidic or more alkaline conditions. For the strain Lalvin EC-1118, it
was observed that the production of ethanol enhanced with the increase in pH of
medium; and it showed that ethanol production was significantly higher (P<0.05) i.e.
9.8% (v/v) when the pH was adjusted at 4.5 (Appendix F1). The further increase in
pH reduced the production of ethanol. Same trend was observed in MZ-4 strain which
showed that the increase in pH enhanced the ethanol content in fermentation medium
up to the pH 5.0. The maximum of 10.2% (v/v) of ethanol was produced at pH 5.0
(P<0.05); however, further increase in pH reduced the ethanol content obtained at the
end of fermentation (Appendix F1). Therefore, it could be concluded from the above
observations that the optimized pH value for both Lalvin EC-118 and MZ-4 was 4.5
and 5.0, respectively.
(b) Effect of Temperature
The effect of temperature on enhanced production of bioethanol by Lalvin EC-1118
and MZ-4 strains was studied in range of 27-39°C (Fig. 4.4, Appendix D2). During
this study, it was investigated that the production of ethanol increased with increase in
temperature; however, there was a certain limit for each microbial strain up to which
the temperature positively affected the activity of each strain. As the temperature
exceeded that specific point, a reduction in ethanol yield was clearly observed. The
study of temperature’s effect on Lalvin EC-1118 showed that the lower temperature
i.e. 27°C was not as effective for ethanol production as it was observed at 30°C;
however, ethanol production was decreased with further increase in temperature
beyond this limit. The production of ethanol was significantly higher (P<0.05) at
30°C for Lalvin EC-1118 strain (Appendix F2). Similar observation was recorded in
case of MZ-4 strain, which showed significantly higher ethanol production (P<0.05)
when the fermentation medium was incubated at 33°C, and the temperature
adjustment below or above 33°C adversely affected the fermentation process
(Appendix F2). Therefore, it was concluded that the optimum production of ethanol
by Lalvin EC-1118 [9.8% (v/v)] and MZ-4 [10.3% (v/v)] was achieved at 30°C and
33°C, respectively.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 74
Fig.4.3: Effect of pH on enhanced production of bioethanol by Lalvin EC-1118 and
MZ-4
Fig. 4.4: Effect of temperature on enhanced production of bioethanol by Lalvin EC-
1118 and MZ-4
0
2
4
6
8
10
12
3 3.5 4 4.5 5 5.5 6
Eth
ano
l % (
v/v)
pH
Lalvin EC-118 MZ4
0
2
4
6
8
10
12
27 30 33 36 39
Eth
ano
l % (
v/v)
Temperature (C)
Lalvin EC-118 MZ4
PhD Thesis
Enhanced production of biofuel from sugar industry waste 75
(c). Effect of Inoculum Size
After allowing the living cells to grow for certain time, different concentration of
exactly measured cell density was inoculated in order to get the highest concentration
of ethanol. The inoculum was added as a liquid culture; therefore, more amount of
inoculum added can dilute the reaction medium in terms of sugar concentration which
in turn reduces the final ethanol concentration. To determine the effect of inoculum
size, the inoculum having 3x108 cells/ml was prepared and the different volumes of
that inoculum in range 2.5-12.5% (v/v) was added in fermentation medium (Figure
4.5, Appendix D.3). It was observed that the production of ethanol was also enhanced
with the increase in inoculum; however, when the inoculum size increased beyond
certain limit, no further increase in ethanol content was observed in fermentation
medium. For the strain Lalvin EC-1118, significantly greater (P<0.05) amount of
ethanol was produced i.e. 10% (v/v), when 7.5% (v/v) of inoculum was added into the
medium. Similarly, 10.5% (v/v) of ethanol was produced when 10.0% (v/v) of MZ-4
inoculum was added into it, which was significantly higher (P<0.05) than other
inoculum sizes (Appendix F3). Further increase or decrease in inoculum reduced the
content of ethanol in fermentation medium.
(d). Effect of Inoculum Age
The effect of inoculum age was studied for both strains i.e. Lalvin EC-1118 and MZ-4
after developing the inoculum for different period of time i.e. 12-48 h (Fig. 4.6,
Appendix D4). Both the strains Lalvin EC-1118 and MZ-4 produced significantly
higher (P<0.05) ethanol of 10% and 10.5% (v/v) respectively when 24 h old inoculum
was used in fermentation medium (Appendix F4). The production was greatly reduced
with further increase in age of inoculum. In case of both strains i.e. MZ-4 and Lalvin
EC-1118, the best inoculum age was determined as 24 h. During inoculum
preparation, both strains after 24 h of incubation reached to actively growing log
phase. These actively growing cells experienced short span lag phase when inoculated
in a reaction flask. After 24 h the strains might be shifted to stationary or death phase
which adversely affected the density of living cells and reduced the ethanol
production.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 76
Fig.4.5: Effect of inoculum size on enhanced production of bioethanol by Lalvin EC-
1118 and MZ-4
Fig. 4.6: Effect of inoculum age on enhanced production of bioethanol by Lalvin EC-
1118 and MZ-4
0
2
4
6
8
10
12
2.5 5 7.5 10 12.5
Eth
ano
l % (
v/v)
Innoculum % (v/v)
Lalvin EC-118 mz4
0
2
4
6
8
10
12
12hours 24hours 36hours 48hours
Eth
ano
l % (
v/v)
Inoculum age
Lalvin EC-118 MZ4
PhD Thesis
Enhanced production of biofuel from sugar industry waste 77
(e). Effect of Nitrogen Sources
To study the effect of different concentration of various nitrogen sources on Lalvin
EC-1118 and MZ-4, different concentrations of urea, ammonium chloride (NH4Cl),
ammonium nitrate (NH4NO3), ammonium sulfate ((NH4)2SO4) and di-ammonium
phosphate ((NH4)2HPO4) were added in fermentation media in range 0.05-0.15%
(w/v) to determine their effect on both of selected strains. The effect of nitrogen strain
on Lalvin EC-1118 is shown in Fig 4.7 and Appendix D5. Ethanol concentration was
increased from 10.1 to 10.2% (v/v) as the urea concentration was increased from 0.05
to 0.10% (w/v) in the medium inoculated with strain Lalvin EC-118. However, further
increase in urea concentration adversely affected the efficiency of this strain and it
reduced the ethanol production. In case of NH4Cl, the increase in its concentration
from 0.05 to 0.15% (w/v) resulted into enhancement in ethanol concentration from
10.1 to 10.4% (v/v). The addition of 0.05 % (w/v) NH4NO3 enhanced the ethanol
yield up to 10.3%; however, the further increase in its concentration reduced ethanol
content. The effect of (NH4)2SO4 on ethanol production was same as for NH4Cl. As
the amount of (NH4)2SO4 increased from 0.5 to 0.15%, the ethanol concentration
increased from 10.0 to 10.4%. The maximum concentration of ethanol was obtained
when (NH4)2HPO4 was added as nitrogen source, i.e., 10.3 to 10.5% ethanol was
produced after addition of 0.05 to 0.1% of (NH4)2HPO4; however, with increase in its
concentration up to 0.15%, the ethanol concentration reduced to 10.0%. After
observing all the data, it was concluded that (NH4)2HPO4 was the comparatively
better nitrogen source for the strain Lalvin EC-118 and it yields significantly higher
(P<0.05) ethanol concentration up to 10.5% (v/v) and required in less amount as
compared to (NH4)2SO4 and NH4Cl; therefore, it was added in fermentation media as
the best nitrogen source for further experiments (Appendix F5).
The effect of different nitrogen sources on enhanced production of bioethanol by MZ-
4 strain was also studied (Fig. 4.7, Appendix D5). It was found that increase in
amount of urea from 0.05 to 0.1% (w/v) in fermentation medium resulted
enhancement in ethanol yield from 10.5 to 10.7% (v/v). However, with further
increase in urea concentration, a decrease in amount of ethanol in fermentation
medium was observed. Similar trend was observed in the case of NH4Cl. An increase
in NH4Cl concentration from 0.05 to 0.1% (w/v) enhanced the ethanol yield from 10.6
to 10.8% (v/v); however, further increase resulted in reduction of ethanol
PhD Thesis
Enhanced production of biofuel from sugar industry waste 78
concentration. The effect of NH4NO3 and (NH4)2HPO4 on ethanol production was
found similar, 10.6% (v/v) of ethanol was produced in the presence of 0.1% (w/v) of
NH4NO3 and (NH4)2HPO4 in fermentation medium. Any increase or decrease in its
concentration reduced the final ethanol content in fermentation medium. In case of
(NH4)2SO4, ethanol concentration was increased from 10.5 to 10.7% (v/v) with an
increase in its concentration from 0.05 to 0.15%. From all the data, it was concluded
that, NH4Cl was the comparatively better nitrogen source for the strain MZ-4, that
could produce significantly higher (P<0.05) ethanol, i.e., 10.8% (v/v) at 0.1% (w/v) of
its concentration (Appendix F.6).
From the above study, it was concluded that the best nitrogen source for strain Lalvin
EC-1118 and MZ-4 was (NH4)2HPO4 and NH4Cl, 0.1% (w/v) of their concentration
resulted into 10.5% and 10.8% (v/v) of ethanol, respectively.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 79
Fig.4.7: Effect of nitrogen source on enhanced production of bioethanol by Lalvin
EC-1118 and MZ-4
0
2
4
6
8
10
12
0.0
5%
0.1
0%
0.1
5%
0.0
5%
0.1
0%
0.1
5%
0.0
5%
0.1
0%
0.1
5%
0.0
5%
0.1
0%
0.1
5%
0.0
5%
0.1
0%
0.1
5%
Urea NH4Cl NH4NO3 (NH4)2SO4 (NH4)2HPO4
Eth
ano
l % (
v/v)
Nitrogen source (% w/v)
Lalvin EC-118
0
2
4
6
8
10
12
0.0
5%
0.1
0%
0.1
5%
0.0
5%
0.1
0%
0.1
5%
0.0
5%
0.1
0%
0.1
5%
0.0
5%
0.1
0%
0.1
5%
0.0
5%
0.1
0%
0.1
5%
Urea NH4Cl NH4NO3 (NH4)2SO4 (NH4)2HPO4
Eth
ano
l % (
v/v)
Nitogen source (% w/v)
MZ-4
PhD Thesis
Enhanced production of biofuel from sugar industry waste 80
(f). Effect of Chelating Agents
The effect of different chelating agents for the enhanced production of bioethanol
showed high significance difference (P<0.05) for the production of bioethanol.
Different types of chelating agents i.e. EDTA, K4Fe(CN)6, and NaK-Tartrate were
added in fermentation medium in concentration 0.0025-0.32 (w/v) (Fig 4.8, Appendix
D6) In case of Lalvin EC-118 strain, it was observed that the increased concentration
of EDTA in fermentation media also enhanced the ethanol yield. The addition of
0.04% (w/v) of EDTA and NaK-tartarate enhanced ethanol yield up to 10.7% (v/v);
however, further increase in its concentration adversely affected the ethanol
production. The maximum amount of ethanol obtained was 10.9% (v/v) when 0.04%
(w/v) of K4Fe(CN)6 was added into fermentation medium., which was significantly
greater (P<0.05) than the effect of other chelating agents (Appendix F7). However,
when the amount of chelating agent was increased more than 0.04% (w/v), it
adversely affected the fermentation process. Therefore; K4Fe(CN)6 was considered as
comparatively better option to be used in fermentation medium as compared to other
chelating agents for strain Lalvin EC-1118.
The effect of various chelating agents on ethanol production from strain MZ-4 was
also observed (Fig 4.8). An increase in ethanol concentration was observed with
increase in concentration of chelating agents. It was observed that the maximum of
10.9% (v/v) ethanol was produced when 0.04% (w/v) of EDTA was added into
fermentation medium, and the further increase or decrease in its concentration lowers
the ethanol production. Similarly, when 0.01% (w/v) of K4Fe(CN)6 was added into
fermentation medium, the production was increased up to the maximum of 11.1%
(v/v), which was significantly higher (P<0.05) than the effect of other chelating
compounds (Appendix F8). In case of NaK-tartarate, 10.9% (v/v) of ethanol was
produced in the presence of only 0.02% (w/v) of the chelating agent and its further
increase in concentration reduced the ethanol content. By comparing the effect of all
three chelating agents, it was concluded that K4Fe(CN)6 was the comparatively better
option to be used in fermentation medium, because it was required in low
concentration and yielded more ethanol as compared to other chelating agents.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 81
0
2
4
6
8
10
120
.00
25
0.0
05
0.0
1
0.0
2
0.0
4
0.0
8
0.1
6
0.3
2
0.0
02
5
0.0
05
0.0
1
0.0
2
0.0
4
0.0
8
0.1
6
0.3
2
0.0
02
5
0.0
05
0.0
1
0.0
2
0.0
4
0.0
8
0.1
6
0.3
2
EDTA K4FE(CN)6 NaK-Tartarate
Eth
ano
l % (
v/v)
Chelating agents ( % w/v)
Lalvin EC-118
0
2
4
6
8
10
12
0.0
02
5
0.0
05
0.0
1
0.0
2
0.0
4
0.0
8
0.1
6
0.3
2
0.0
02
5
0.0
05
0.0
1
0.0
2
0.0
4
0.0
8
0.1
6
0.3
2
0.0
02
5
0.0
05
0.0
1
0.0
2
0.0
4
0.0
8
0.1
6
0.3
2
EDTA K4Fe(CN)6 NaK-Tartarate
Eth
anl (
% v
/v)
Chelating agents (%w/v)
MZ-4
PhD Thesis
Enhanced production of biofuel from sugar industry waste 82
Fig.4.8: Effect of chelating agents on enhanced production of bioethanol by Lalvin
EC-1118 and MZ-4
Fermentation Efficiency after Optimization
Fermentation efficiency of the process was determined again after optimization of
process and an increase in fermentation efficiency was noted (Table 4.4). It was
observed that the fermentation efficiency of strain Lalvin EC-118 was calculated as
60.0% with 9.6% (v/v) of bioethanol at 25% (w/v) of sugar concentration; however,
the efficiency was increased to 68.1% with 10.9% (v/v) of ethanol production after
optimization of physicochemical parameters utilizing same sugar concentration. In
case of MZ-4 strain, fermentation efficiency before optimization was calculated as
63.1% with 10.2% (v/v) ethanol yield with 25% (w/v) of sugar; however after
optimization it was increased up to 69.3% with 11.1% (v/v) ethanol yield with same
sugar concentration.
Table.4.4: Enhancement of fermentation efficiency due to optimization
Strains
Before optimization After optimization
Ethanol
Yield % (v/v)
Fermentation
Efficiency (%)
Ethanol
Yield % (v/v)
Fermentation
Efficiency (%)
Lalvin EC-
1118
9.6±0.16 60.0 10.2±0.16 68.1
MZ-4 10.1±0.12 63.1 11.1±0.16 69.3
4.3. FED BATCH FERMENTATION
During fed batch fermentation, substrate was added after specific intervals in order to
reduce the osmotic pressure of the fermentation medium faced by fermenting
microbes. The effect of specific gravity and feeding interval on enhanced production
of bioethanol was also studied. Those conditions were preferred for fed batch
fermentation which showed enhanced ethanol production and better fermentation
efficiency. The process completion time for each step was also determined because of
the time-constrained issues faced by industry.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 83
4.3.1. Effect of Specific Gravity
The specific gravity was adjusted within range of 1.080-1.140 in order to determine
the best specific gravity for the fed-batch fermentation using strains Lalvin EC-118
and MZ-4 (Fig. 4.9). For the Lalvin EC-118, it was observed that the increase in
specific gravity positively affected on production of ethanol. This strain produced
significantly greater (P<0.05) ethanol, when specific gravity was adjusted to 1.090
(Appendix F9). The production of ethanol at specific gravity of 1.080 was determined
as 11.7% (v/v) that was increased to 13.9% with increase in gravity up to 1.090. No
increase in ethanol yield was observed with further increase in specific gravity beyond
this point. The higher initial specific gravity of fermentation media increased the
osmotic pressure, and hence decreased the ethanol yield. The use of very high gravity
molasses i.e. 1.140 reduced the ethanol yield up to 9.7% (v/v).
In case of strain MZ-4 for fed batch fermentation, ethanol production was increased
from 12.5 to 13.5% (v/v) with the increase in specific gravity from 1.080 to 1.090.
Thus again it was observed that MZ-4 strain produced significantly greater (P<0.05)
ethanol, when specific gravity was adjusted to 1.090 (Appendix F10). The further
increase in specific gravity reduced the final ethanol concentration. Similar to Lalvin
EC-118 strain, the production of ethanol reduced to 9.6% (v/v) by using very high
gravity molasses i.e. 1.140. All these observation showed that 1.090 was the best
specific gravity in case of fed batch fermentation which was easily tolerated by
fermenting microbes and it showed enhanced ethanol production.
4.3.2. Effect of Viscosity
The viscosity of each molasses dilution was determined and it was observed that the
viscosity increases with the increase in amount of molasses, which can create an
unfavorable environment for the growth and productivity of microbial strains. The
viscosity of all the molasses dilutions were determined as mentioned in Table 4.5 and
4.6. The lowest viscosity was determined at the specific gravity of 1.080 as 1.86mP-s,
whereas with the increase in specific gravity an increase in viscosity was also noted.
The maximum viscosity of 4.06mP-s was determined with the highest specific gravity
1.040 used in this study. The result revealed that, high osmotic pressure is not the only
bottleneck of the high gravity fermentation process, but the increase in viscosity was
PhD Thesis
Enhanced production of biofuel from sugar industry waste 84
also related to high molasses content that can create an unfavorable environment for
the growth of fermenting microorganisms.
4.3.3. Effect of Feeding Rate
The molasses was fed after various intervals to determine the exact feeding rate for
the maximum production of ethanol at any specific gravity (Fig. 4.9). In case of
Lalvin EC-1118, no regular trend in ethanol production was observed with the
difference in feeding interval; however, in most cases it was observed that more delay
in feeding time decreased the production of ethanol. From the Fig 4.8, it was inferred
that the feeding interval of 12 h at optimized specific gravity i.e. 1.090, the ethanol
content was enhanced up to 13.9% (v/v); however, at the same specific gravity, the
ethanol content reduced to 10.2% (v/v) when feeding was done after every 48 h. The
lowest content of ethanol was determined as 8.3% (v/v) at specific gravity of 1.140 at
feeding rate of 48 h, which showed that the higher specific gravity and delayed
feeding rate adversely affected the production of bioethanol.
In case of strain MZ-4, it was observed that there was no regular trend in increase in
ethanol yield; however, in most cases 24 h was considered as the best feeding interval
to get the enhanced production of ethanol. It was observed that the maximum of
13.5% (v/v) of ethanol was produced when specific gravity was adjusted at optimized
value i.e. 1.090 and fed after every 24 h. It was also observed in most cases that the
delay in feeding time reduced the concentration of ethanol in fermentation medium.
The comparison of both strains showed that the commercial strain Lalvin EC-1118
was more active, and rapidly converted sugars into ethanol; however, strain MZ-4
required more time for the conversion of sugars into ethanol.
Fermentation Efficiency
The fermentation efficiency of the fed batch process at different specific gravity of
molasses with different feeding rate was determined for both strains i.e. Lalvin EC-
1118 and MZ-4. It was observed that higher specific gravity and long feeding
intervals had negative impact on actual ethanol yield, thus reduced the fermentation
PhD Thesis
Enhanced production of biofuel from sugar industry waste 85
efficiency of the process. For Lalvin EC-1118, it was observed that maximum ethanol
production was obtained at 1.090 specific gravity with 12 h feeding rate and
maximum fermentation efficiency i.e. 81.1% was noted (Table 4.5). In case of strain
MZ-4, maximum ethanol yield was obtained at specific gravity 1.090 with 24 h
feeding interval, and maximum fermentation efficiency of 83.2% was also observed
under same conditions (Table 4.6).
Process completion time
Process completion time is one of the important factors to determine in case of fed-
batch fermentation as it directly depends on feeding rate and most of the ethanol
industries face the problem of time constraint. The completion time of the process at
different conditions by using strain Lalvin EC-1118 is shown in Table. 4.5. It was
observed that the maximum quantity of ethanol from strain Lalvin EC-118 was 13.9%
with 81.1% fermentation efficiency within 84 h. In case of MZ-4 strain, the process
completion time under different conditions is shown in Table. 4.6. The maximum
amount of ethanol obtained from strain MZ-4 was 13.5% (v/v) exhibiting 83.2%
fermentation efficiency within 120 h.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 86
Fig.4.9: The effect of specific gravity and feeding rate for enhanced production of
bioethanol during fed-batch fermentation using strains Lalvin EC-1118 and MZ-4
0
2
4
6
8
10
12
14
16
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
1.080 1.090 1.100 1.110 1.120 1.130 1.140
Eth
anl(
v/v)
%
Feeding intervals at different specific gravity
Lalvin EC 118
0
2
4
6
8
10
12
14
16
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
12
hrs
.
24
hrs
.
36
hrs
.
48
hrs
.
1.080 1.090 1.100 1.110 1.120 1.130 1.140
Eth
ano
l (v/
v) %
Feeding intervals at different specific gravity
MZ-4
PhD Thesis
Enhanced production of biofuel from sugar industry waste 87
Table.4.5: The effect of specific gravity and feeding rate of molasses on fermentation
efficiency and process completion time of fed batch fermentation using Lalvin EC-
1118.
Specific
Gravity
Viscosity
(milliPascal-
second)
Sugar
Conc.
% (w/v)
Feeding
Time
(h)
Actual
Ethanol
%(v/v)
Fermentation
Efficiency
(%)
Process
Completion
time (h)
1.080 1.86 15 12 11.5 75.9 60
1.080 1.86 15 24 11.7 80.4 96
1.080 1.86 15 36 10.3 74.5 120
1.080 1.86 15 48 9.6 64.4 144
1.090 2.13 17 12 13.9 81.1 84
1.090 2.13 17 24 12.5 78.4 120
1.090 2.13 17 36 11.1 71.8 108
1.090 2.13 17 48 10.2 64 144
1.100 2.34 19 12 13 71.1 96
1.100 2.34 19 24 10.9 60 72
1.100 2.34 19 36 11 60.6 108
1.100 2.34 19 48 9.9 53.9 144
1.110 2.86 21 12 10.7 59.7 72
1.110 2.86 21 24 12.2 64 96
1.110 2.86 21 36 11 56.4 108
1.110 2.86 21 48 10.1 50.7 96
1.120 3.20 23 12 11.9 50.5 84
1.120 3.20 23 24 9.4 37.1 96
1.120 3.20 23 36 10.3 44.3 108
1.120 3.20 23 48 10.2 69.0 96
1.130 3.60 25 12 8.6 41.4 96
1.130 3.60 25 24 10.4 51.3 96
1.130 3.60 25 36 10.2 52.1 108
1.130 3.60 25 48 9.9 47.5 96
1.140 4.06 27 12 9.1 42.3 96
1.140 4.06 27 24 9.1 41.0 96
1.140 4.06 27 36 9.7 45.1 108
1.140 4.06 27 48 8.2 36.4 96
PhD Thesis
Enhanced production of biofuel from sugar industry waste 88
Table.4.6: The effect of specific gravity and feeding rate of molasses on fermentation
efficiency and process completion time of fed batch fermentation using MZ-4
Specific
Gravity
Viscosity
(milliPascal-
second)
Sugar
Conc. %
(w/v)
Feeding
Time
(h)
Actual
Ethanol
%
(v/v)
Fermentati
on
Efficiency
(%)
Process
Completion
time (h)
1.080 1.86 15 12 12.1 81.4 84
1.080 1.86 15 24 12.5 81.7 96
1.080 1.86 15 36 10.8 67.7 120
1.080 1.86 15 48 9.6 65.4 144
1.090 2.13 17 12 12.5 78.8 84
1.090 2.13 17 24 13.5 83.2 120
1.090 2.13 17 36 10.3 68.6 108
1.090 2.13 17 48 10 67.7 144
1.100 2.34 19 12 12 75.4 60
1.100 2.34 19 24 12.4 72.1 96
1.100 2.34 19 36 11.6 64.8 108
1.100 2.34 19 48 10.6 62.6 144
1.110 2.86 21 12 12 64.2 72
1.110 2.86 21 24 12.6 68.9 96
1.110 2.86 21 36 11.4 61 72
1.110 2.86 21 48 10 52 144
1.120 3.20 23 12 9.2 46.3 84
1.120 3.20 23 24 11.4 59.8 96
1.120 3.20 23 36 10.6 56 108
1.120 3.20 23 48 9.1 45.5 96
1.130 3.60 25 12 10.4 50 72
1.130 3.60 25 24 10.8 53.4 96
1.130 3.60 25 36 9.1 44.1 108
1.130 3.60 25 48 8.3 40.9 96
1.140 4.06 27 12 9.2 41.8 84
1.140 4.06 27 24 9 39.9 96
1.140 4.06 27 36 9.5 44.2 108
1.140 4.06 27 48 8.2 37.3 96
PhD Thesis
Enhanced production of biofuel from sugar industry waste 89
PART-B: ENHANCED PRODUCTION OF BIOETHANOL FROM
SUGARCANE BAGASSE
Sugarcane bagasse is the second major type of waste generated by sugar industry.
During this part of study, sugarcane was pretreated by different methods i.e.
autohydrolysis and ionic liquid pretreatment. In next section, the chemical and
structural composition of both types of pretreated bagasse was determined in
comparison to their respective controls. After that, the pretreated bagasse was
subjected to enzymatic hydrolysis with their optimized enzyme loading amount. In
last step, both types of pretreated bagasse was subjected to fermentation by four
different types of yeast strains, to determine the bioethanol produced from each type
of pretreated bagasse.
4.4. BIOMASS PREPARATION
The sugarcane bagasse was dried and milled up to the size of 0.45mm as shown in
Fig.4.10.
4.5. PRETREATMENT OF SUGARCANE BAGASSE
(i) Autohydrolysis
The milled sugarcane bagasse was autohydrolyzed at 190°C for 10 min and 205° C
for 6 min. The bagasse obtained after pretreatment was shown in figure 4.11(a). In the
figure, it could be observed that there was color variation in bagasse pretreated at
various conditions. The increased intensity in color and less porous texture of bagasse
was observed with increase in pretreatment temperature of autohydrolysis.
(ii) Ionic liquid (IL) Pretreatment
The milled sugarcane bagasse was pretreated with IL at 110°C for 30 min. Untreated
bagasse and the bagasse treated with water under same conditions were considered as
control. The bagasse obtained after pretreatment was shown in figure 4.11(b). The
bagasse pretreated with water at 110ºC for 10 minutes showed similarity in color and
texture with the untreated bagasse. However, the IL-pretreated bagasse showed more
dark color that revealed the removal of lignin during pretreatment.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 90
Fig.4.10: Drying and milling of sugarcane bagasse through 40 Mesh sieve size: before
drying and milling (left); after drying and milling (right)
Fig.4.11 (a): Sugarcane bagasse autohydrolyzed at 190°C for 10 min; 205°C for 6
min and untreated bagasse control
PhD Thesis
Enhanced production of biofuel from sugar industry waste 91
Fig.4.11(b): Sugarcane bagasse, IL pretreated at 110°C for 30 min; water treated at
110°C for 30 min (control) and untreated bagasse (control)
4.5.1. Severity Factor
(i). Autohydrolysis
Sugarcane bagasse was pretreated with autohydrolysis, and the severity of each
pretreatment reaction was determined as shown in Table 4.7(a). The severity factor
determined for this autohydrolysis pretreatment at 190ºC for 10 min and 205ºC for 6
min was 3.64 and 3.86, respectively.
Table 4.7(a): Severity factors for different conditions of autohydrolysis
Pretreatment Temperature Time Severity Factor
Untreated Bagasse - - -
Autohydrolysis 190 °C 10 min. 3.64
Autohydrolysis 205 °C 6 min. 3.86
(ii). Ionic liquid Pretreatment
The severity factor for IL pretreatment was determined and shown in Table 4.7(b).
The severity factor for ionic liquid pretreatment and its water treated control at 110ºC
for 30 min was same i.e. 1.77 because same pretreatment conditions were used to
determine the difference in different pretreatments.
Table 4.7(b): Severity factors for IL pretreatment conditions
Pretreatment Temperature Time Severity Factor
Untreated Bagasse - - -
Water-treated
control
110 °C 30 min. 1.77
Ionic liquid
[C4mim][OAc]
pretreatment
110 °C 30 min. 1.77
PhD Thesis
Enhanced production of biofuel from sugar industry waste 92
4.6. COMPOSITIONAL ANALYSIS OF SUGARCANE BAGASSE
4.6.1. Lignin Determination
(i). Autohydrolyzed Bagasse
The effect of autohydrolysis on lignin content of bagasse was shown in Table 4.8(a).
The lignin determination of sugarcane bagasse showed that the total amount of lignin
present in untreated bagasse was 31.9%, with 27.5% of acid insoluble (klason lignin)
and 4.4% of acid soluble lignin. After autohydrolysis of sugarcane bagasse at 190°C
for 10 min, the acid soluble lignin (Klason lignin) was increased to 37.7% which
increased the total lignin content to 41.8%; however, the acid soluble lignin was
reduced to 3.1%. Same trend was observed after autohydrolysis at 205°C for 6 min
that the klason lignin was increased from 27.5 to 36.0% due to which the total lignin
was increased from 31.9 to 39.4%, whereas acid soluble lignin was reduced to 3.4 %.
Table 4.8(a): Lignin Determination of Autohydrolyzed Sugarcane bagasse
Pretreatment Temperature Time Klason
lignin ASL
Total
Lignin
Untreated control - - 27.5±0.2 4.4±0.1 31.9±0.4
Autohydrolysis 190 °C 10 min 37.7±0.3 3.1±0.2 41.8±0.7
Autohydrolysis 205 °C 6 min 36.0±0.4 3.4±0.1 39.4±0.7
ASL= acid soluble lignin
(ii). Ionic liquid Pretreated Bagasse
During current study, the content of lignin was reduced from 31.9% to 28.3% after IL
pretreatment (Table 4.8b). The amount of klason lignin was actually reduced from
27.5 to 21.3% in IL-pretreated sample; however, the overall increase in lignin content
was observed due to increase in acid soluble lignin from 4.4 to 8.0%. The lignin
content in water treated control remained almost same as untreated control. The total
lignin content in water treated bagasse was reduced from 31.9% to 30.9%; and the
PhD Thesis
Enhanced production of biofuel from sugar industry waste 93
amount of klason lignin and acid soluble lignin was reduced from 27.5 to 26.8% and
4.4 to 4.1%, respectively, which was not a noticeable difference as compared to IL
pretreated sample.
Table 4.8(b): Lignin determination of IL pretreated sugarcane bagasse
Pretreatment Temp. Time Klason
lignin
ASL Total
Lignin
Untreated Control - - 27.5±0.2 4.4±0.1 31.9±0.4
Water-Treated
Control 110 °C 30 min 26.8±0.2 4.1±0.1 30.9±0.4
IL-pretreated
Bagasse 110 °C 30 min 21.3±0.1 8.0±0.2 28.3±0.4
ASL= acid soluble lignin
4.6.2. Carbohydrate Determination
The carbohydrate content was determined by HPLC and the effect of pretreatments on
the compositional changes was analyzed. The Figure 4.12 is the chromatogram which
showed the peak of glucose, xylose, arabinose and mannose with retention time of 29,
32, 37 and 39 min, respectively. The area of peaks was compared with standard curve
formulated by plotting the graph of different concentration of sugars against area of
defined peak (Appendix C).
PhD Thesis
Enhanced production of biofuel from sugar industry waste 94
Fig. 4.12: Chromatogram showing peak of glucose, xylose, arabinose and mannose
standard (with retention time of 29, 32, 37 and 39 min respectively)
PhD Thesis
Enhanced production of biofuel from sugar industry waste 95
(i). Autohydrolyzed Bagasse
The effect of different pretreatment strategies on composition of sugarcane bagasse
was shown in Table 4.9(a). It was observed that the glucan content in untreated
bagasse was noted as 37.7%; however, this amount increased to 47.7 and 51.2% in
samples autohydrolyzed at 190°C for 10 min and 205°C for 6 min. The increase in
cellulose content in bagasse might be due to removal of other components. The xylan
content in untreated bagasse was determined as 18.5% which was reduced to 8.2 and
3.8% in autohydrolyzed at 190 and 205 °C respectively. Similar removal of arabinan
was detected during autohydrolysis, and its amount was decreased from 0.1 to 0.04%
in sample autohydrolyzed at 190°C. In the sample autohydrolyzed at 205°C, arabinan
was removed to the extent that it couldn’t be quantified by HPLC. The quantity of
mannan was quantified as 0.004 % only in the sample pretreated at 205°C. In other
samples mannan could not be quantified; therefore, the effect of pretreatment on
mannan changes could not be determined. In addition, no peak for galactan could be
observed in bagasse sample.
Table 4.9(a): Carbohydrate determination of autohydrolyzed sugarcane bagasse
Pretreatme
nt
Temp Time Glucan
%
Xylan
%
Arabinan
%
Mannan
%
Untreated
control
- - 37.7±0.7 18.5±0.3 0.1±0.0 N.Q
Autohydrolysis 190°C 10 min 47.7±0.6 8.2±0.4 0.04±0.1 N.Q
Autohydrolysis 205°C 6 min 51.2±0.3 3.8±0.1 N.Q 0.004±0.0
N.Q=not quantified
(ii). Ionic Liquid Pretreated Bagasse
The carbohydrate content of IL pretreated bagasse in comparison to untreated and
water treated control is shown in Table.4.9 (b). It was observed that the glucan
PhD Thesis
Enhanced production of biofuel from sugar industry waste 96
content in untreated bagasses was 37.7% and it was reduced to 37.2% in IL-pretreated
sample. Similarly, in water treated control the difference was quite negligible i.e.
38.5% glucan. The xylan content in IL –pretreated bagasse also reduced from 18.5 to
12.3%; however, the content of xylan was increased in water treated control sample.
The content of arabinan was also increased after pretreatment from 0.1 to 6.07% and
7.0% in case of water treated control and IL pretreated bagasse samples, respectively.
Mannan was quantified as 0.1% in both pretreated samples, but it couldn’t be
quantified in untreated bagasse sample. The galactan was not determined in any of
these samples.
Table.4.9.b: Carbohydrate determination of IL pretreated sugarcane bagasse
Pretreatment Temp Time Glucan
%
Xylan
%
Arabinan
%
Mannan
%
Untreated
control - - 37.7±0.7 18.5±0.3 0.1±0.0 N.Q
Water Treated
Control 110°C 30 min 38.5±0.0 18.9±0.4 6.07±0.1 0.1±0.0
IL-pretreated
bagasse 110°C 30 min 37.2±1.0 12.3±1.0 7.0±0.0 0.1±0.0
4.7. EFFECT OF PRETREATMENT ON BIOMASS STRUCTURE
4.7.1. Fourier Transform Infrared Spectroscopy (FTIR)
Attenuated total reflection-Fourier transform infrared (ATR–FTIR) spectroscopy was
conducted and different absorption bands were used to monitor the chemical changes
of lignin and carbohydrates.
Table 4.10: Assignments of FTIR-ATR absorption bands for bagasse
Wavelength
(cm-1
)
Assignment of Peaks
3336 O-H stretching, related to cellulose-hydrogen bonds
2916 C-H stretching, related to biomass methyl/methylene group
1604 Lignin aromatic ring stretch mode
1635 Ring-conjugated C=C bond in coniferaldehyde
1514 Aromatic skeletal from lignin
1424 CH2 scissor motion in cellulose
1370 C–H stretch in cellulose and hemicellulose
PhD Thesis
Enhanced production of biofuel from sugar industry waste 97
1243 Acetylated hemicellulose
1103 Crystalline cellulose
898 Amorphous components
(Adapa et al., 2011; Sun et al., 2015)
(i). Autohydrolyzed Bagasse
The FTIR spectrum of autohydrolyzed bagasse sample is shown in Fig. 4.13(a). The
decrease in spectral intensity at 3300cm-1
showed reduction in cellulose hydrogen
bonding. Two main lignin features were monitored that correspond to lignin aromatic
ring stretch mode (1604 cm-1
) and ring-conjugated C=C bond in conifer aldehyde
(1635 cm-1
), respectively. High temperature autohydrolysis clearly showed
diminished C=C bond in conifer aldehyde, as indicated by peak at 1631 cm-1
, and also
significant modification of the aromatic ring which exhibited the removal of lignin
aromatic ring stretch. Similarly, the significant peaks at 1514 cm-1
(aromatic skeletal
from lignin) were observed for all the autohydrolyzed samples, which might be due to
removal of large content of hemicellulose during autohydrolysis from sugarcane
bagasse sample. A significant peak at 1370 cm-1
(C–H stretch in cellulose and
hemicellulose) in samples obtained after autohydrolysis was likely due to the removal
of major hemicelluloses which comparatively increased the cellulose content in
bagasse, as also determined during compositional analysis. The reduction in peak at
1243 in autohydrolyzed samples showed the reduction in acetylated hemicelluloses.
The peak intensity at 1103 (crystalline cellulose) and peak reduction at 898
(amorphous cellulose) clearly showed the increase in crystallinity of autohydrolyzed
sugarcane bagasse.
(ii) Ionic liquid Pretreated Bagasse
The FTIR spectrum of autohydrolyzed bagasse sample is shown in Fig. 4.13(b). The
increase in spectral intensity at 3300cm-1
in ionic liquid treated bagasse showed
reduction in cellulose hydrogen bonding. The reduction in lignin aromatic ring stretch
mode (1604 cm-1
) and ring-conjugated C=C bond in conifer aldehyde (1635 cm-1
)
showed the removal of lignin component from IL treated sample; however, these two
peaks were increased in water treated control. A significant increase in peak at 1370
cm-1
(C–H stretch in cellulose and hemicellulose) was likely due to the removal of
major hemicelluloses which comparatively increased the cellulose content in bagasse.
The reduction in peak intensity at 1243 cm-1
in IL pretreated bagasse demonstrated the
PhD Thesis
Enhanced production of biofuel from sugar industry waste 98
good effect of this pretreatment strategy on removal of acetylated hemicellulose. The
peak at 1103 cm-1
(referring to crystalline cellulose) was diminished after ionic liquid
pretreatment indicated that IL played major role to decrease the cellulose crystallinity.
These results clearly demonstrated that both pretreatments effectively weakened the
van der Waals interaction between cell wall polymers.
4.13 (a): FTIR spectra of untreated, autohydrolysis and IL ([C4mim][OAc]) pretreated
bagasse from 1800-600 cm-1
region
PhD Thesis
Enhanced production of biofuel from sugar industry waste 99
4.13 (b): FTIR spectra of untreated, autohydrolysis and IL ([C4mim][OAc])
pretreated bagasse from 4000 to 1800 cm-1
region
4.7.2. XRD Analysis
XRD analysis was performed to examine the cellulose crystallinity index of biomass.
The X-Ray diffraction patterns of pretreated and untreated bagasse were determined
and two diffraction regions were noticed at 22 (2θ) and 19 (2θ) which corresponds to
I002 (crystalline region) and Iam (amorphous region), respectively to calculate the
crystallinity index.
(i). Autohydrolyzed Bagasse
The XRD analysis of autohydrolyzed samples didn’t show any major difference in
peaks at 22° and 15° (Fig 4.14.a). The valley between these two peaks also didn’t show
any remarkable difference among these peaks.
(ii). Ionic Liquid Treated Bagasse
From the Fig. 4.14(b), a remarkable difference in diffraction pattern was observed in
sugarcane bagasse after IL pretreatment. Diffraction pattern of IL pretreated sample
showed the disappearance of secondary peak (I101) at 2θ value of 15 , and the
crystallinity peak (I002) at 22° was also found to be weaken that represented the profile
PhD Thesis
Enhanced production of biofuel from sugar industry waste 100
of nearly amorphous cellulose. In addition, the broadening of amorphous valley
between the crystalline and secondary peak was also observed.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 101
4.14. XRD analysis of untreated, autohydrolyzed and IL pretreated bagasse
PhD Thesis
Enhanced production of biofuel from sugar industry waste 102
Crystallinity Measurement of Autohydrolyzed and IL-Pretreated Bagasse
In order to determine the crystallinity aspect from FTIR analysis, the peak heights
were used as quantitative parameter as stated by Adapa et al. (2011). In order to
determine the crystallinity of cellulose structure, the ratio at the peak intensities at
1424/898 cm-1
was determined, which was referred as an empirical crystallinity index
proposed by Nelson and O’Connor or Lateral order index (LOI) which has been used
to show the presence of cellulose I structure in cellulose material. The ratio of
1370/2916 cm-1,
also proposed by Nelson and O’Connor (1964), known as total
crystallinity index (TCI), was used to evaluate the infrared crystallinity (IR) ratio.
Thus, the higher values of both LOI and TCI are indicative of the more ordered
structure of cellulose and higher crystallinity of biomass. A great reduction in LOI
and TCI of IL-pretreated sample indicated the reduction in crystallinity of cellulose
(Table 4.11). The order of crystallinity determined by LOI was 205ºC > 190ºC >
110ºC > untreated bagasse >IL pretreated bagasse which also corroborated with the
CrI (crystallinity index) determined by XRD analysis (Table 4.11). Crystallinity index
(CrI) of untreated bagasse samples was determined as 0.61, whereas CrI of the
samples autohydrolyzed at 110˚C, 190˚C and 205˚C was 0.62, 0.65 and 0.68,
respectively (Table 4.11). The CrI of IL treated sample was observed as 0.25 which
exhibited reduction in cellulose crystallinity in bagasse.
Table 4.11: Crystallinity measurements of autohydrolyzed and IL pretreated bagasse
Samples FTIR Crystallinity Ratio Crystallinity
Index (CrI)
based on
XRD
Lateral order
index (LOI)
(1424 cm-1
/898
cm-1
)
Total crystallinity
index (TCI)
(1370 cm-1
/2916 cm-1
)
Untreated bagasse 0.47 ±0.0 0.65 ±0.00 0.61
utoh drol sis
for 10 min) 0.78 ±0.03 0.61 ± 0.04 0.65
utoh drol sis
for 6 min) 1.11 ±0.02 0.55 ±0.02 0.68
Ionic liquid (IL) treated
for min 0.24 ±0.01 0.47 ±0.02 0.25
ater treated-control
for min 0.56 ±0.01 0.76 ±0.01 0.62
PhD Thesis
Enhanced production of biofuel from sugar industry waste 103
4.8. ENZYMATIC SACCHARIFICATION
4.8.1. Enzyme Loading Optimization
(i). Autohydrolyzed Bagasse
The optimized amount of enzyme that is required by a specific pretreated sample to
convert maximum of carbohydrates in to reducing sugars was determined. This is an
important parameter to reduce the cost of process because this makes it possible to
add only required amount of enzyme for the saccharification process and it would
make the process more economically feasible. For the autohydrolyzed samples the
bagasse treated at 190°C was taken as standard for enzymatic loading optimization
and it was observed that with the increase in enzymatic loading (i.e. cellulases and
beta-glucosidases ratio) the amount of released reducing sugar was also increased.
The addition of 5FPU cellulases with 10IU β-glucosidases released 2.7 mg/ml of the
reducing sugar. When increase concentration of enzyme i.e. 10FPU cellulases with
20IU β-glucosidases was added, the amount of released reducing sugars was increased
up to 3.1 mg/mL; however, no further increase in sugar was observed on further
increase in enzyme loading (Fig.4.15.a). Therefore, 10FPU cellulases with 20IU β-
glucosidases was selected to carry out further experimentations. These results showed
that, 10FPU cellulases with 20IU β-glucosidases were the maximum amount of
enzyme which was required for the maximum conversion of cellulose and
hemicellulose into monomeric reducing sugars.
(ii). Ionic liquid Pretreated Bagasse
It was observed during enzyme loading optimization of IL-pretreated sample that the
addition of 5FPU cellulases with 10IU β-glucosidases released 5.0 mg/ml of the
reducing sugar. When increase concentration of enzyme i.e. 10FPU cellulases with
20IU β-glucosidases was added, the amount of released reducing sugars was increased
up to 5.3 mg/mL. However, enzyamatic hydrolysis of IL-pretreated sample with
20FPU of cellulases with 40IU of β-glucosidases released maximum of 6mg/mL of
reducing sugars, which was detected by DNS method. No further increase in reducing
sugar was observed with further increase in enzyme loading (Fig.4.15.b). An
interesting observation was that, IL pretreated sample required more enzyme loading
and released more amount of sugar as compared to autohydrolyzed sample.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 104
Fig.4.15(a): Enzyme loading optimization for autohydrolyzed samples
Fig.4.15 (b): Enzyme loading optimization for IL pretreated samples
0
0.5
1
1.5
2
2.5
3
3.5
0 24 hrs 48 hrs 72 hrs
Re
du
cin
g su
gar
(mg/
ml)
Time (h)
5FPU Cellulases : 10IU B-glucosidases
10FPU Cellulases:20IU B-glucosidases
20FPU Cellulases.:40IUB-glucosidase
0
1
2
3
4
5
6
7
0 24 48 72
red
uci
ng
suga
r (m
g/m
l)
Time (hrs)
5FFPU Cellulase:10IUB-glucosidases 10FPU Cellulases:20IU B-glucosidases
20FPU Cellulase.:40IU B-glucosidase 40FPU Cellulase: 80IU B-glucosidase
PhD Thesis
Enhanced production of biofuel from sugar industry waste 105
4.8.2. Enzymatic Hydrolysis
Fig.4.16: Chromatogram of sugarcane bagasse hydrolysate obtained after enzymatic
hydrolysis
PhD Thesis
Enhanced production of biofuel from sugar industry waste 106
During enzymatic hydrolysis, the release of glucose and xylose were determined by
HPLC. The chromatogram showed the glucose and xylose peaks at retention time of
29 and 32min respectively (Fig 4.16). The area of peaks was compared with standard
curve formulated by plotting the graph of different concentration of sugars against
areas of defined peak (Appendices C).
(i) Autohydrolyzed Bagasse
The variation in glucose concentration released by enzymatic hydrolysis of sugarcane
bagasse pretreated with different strategies was shown in Fig. 4.17.a and Appendix
E.1.1. It was observed that, from an untreated bagasse 0.47mg/ml of glucose was
released after 72 h of enzymatic hydrolysis; however, when the bagasse was
pretreated at 190ºC for 10 min and 205ºC for 6 min, the glucose concentration was
noted as 2.3 mg/ml and 3.5 mg/ml, respectively. These findings showed that the
release of glucose from bagasse pretreated at 205°C was significantly higher (P<0.05)
than other autohydrolyzed bagasse samples (Appendix G1). The amount of xylose
released after enzymatic hydrolysis of various autohydrolyzed was shown in Fig.
4.17.b and Appendix E.1.3. The released xylose concentration from bagasse
pretreated at 190°C was significantly greater (P<0.05) than other autohydrolyzed
samples (Appendix G2). It was determined that the release of xylose from untreated
bagasse was 0.03mg/ml; however, the autohydrolyzed bagasse at 190°C for 10 min
and 205°C for 6 min released 0.4mg/ml and 0.24mg/ml of xylose, respectively.
(a).Cellulose Digestibility (%)
The cellulose digestibility of autohydrolyzed and untreated bagasse was determined
by dividing the amount of cellulose digested by total amount of cellulose present in
pretreated sample. It was observed that the autohydrolyzed samples at 190ºC for 10
min and 205ºC for 6 min showed cellulose digestibility of 46.9% and 62.1% after 72 h
of enzymatic hydrolysis; however, untreated bagasse showed cellulose digestibility of
only 11.4% (Fig. 4.18.a, Appendix E.1.2).
(b). Xylan Digestibility (%)
The hydrolytic process of autohydrolyzed samples was completed at 72 h and xylan
digestion was determined by dividing the amount of xylan digested over the total
amount of xylan in pretreated sample. The figure 4.8.b showed that 4.6% and 5.7%
xylan digestibility was noted in samples autohydrolyzed at 190ºC and 205ºC,
respectively; however, only 1.4% xylan digestibility was determined in untreated
bagasse sample (Appendix E.1.4).
PhD Thesis
Enhanced production of biofuel from sugar industry waste 107
Fig.4.17.a. Glucose concentration released from autohydrolyzed samples during
enzymatic hydrolysis
Fig.4.17(b): Xylose concentration released from autohydrolyzed samples during
enzymatic hydrolysis
0
0.5
1
1.5
2
2.5
3
3.5
4
0 24 48 72
glu
cose
(m
g/m
l)
Time (hrs) Untreated ControlAutohydrolyzed 190 C-10 minAutohydrolyzed 205 C-6 min
0
0.1
0.2
0.3
0.4
0.5
0.6
0 24 48 72
Xyl
ose
(m
g/m
l)
Time (hrs)
Autohydrolyzed 190 C-10 min
Autohydrolyzed 205 C-6 min
Untreated Control
PhD Thesis
Enhanced production of biofuel from sugar industry waste 108
Fig.4.18 (a): Cellulose digestibility from autohydrolyzed samples during enzymatic
hydrolysis
Fig 4.18 (b): Xylan digestibility from autohydrolyzed samples during enzymatic
hydrolysis
0
10
20
30
40
50
60
70
0 24 48 72
Ce
llulo
se d
ige
stib
ility
pe
rce
nta
ge
Time (hrs) Untreated Control
Autohydrolyzed 205 C-6 min
Autohydrolyzed 190 C-10 min
0
1
2
3
4
5
6
7
0 24 48 72
Xyl
an D
ige
stib
lity
(%)
Time (hrs)
Untreated Control
Autohydrolyzed 190 C-10 min
Autohydrolyzed 205 C-6 min
PhD Thesis
Enhanced production of biofuel from sugar industry waste 109
(ii) Ionic liquid Pretreated Bagasse
The variation in glucose and xylose concentration released by enzymatic hydrolysis of
sugarcane bagasse pretreated with IL was shown in Fig 4.19.a (Appendix E.2.1).
Enzymatic saccharification of the IL pretreated bagasse (at 110ºC for 30 min) released
4.0 mg/ml glucose, untreated and water treated control showed the release of 0.47 and
0.8mg/ml of glucose respectively after 72 h of enzymatic hydrolysis. The release of
xylose from IL-pretreated sample was determined as 0.4 mg/ml; however the release
of xylose from water treated control and untreated control was determined as 0.1 and
0.03 mg/ml after 72 h of enzymatic hydrolysis (Fig 4.19.b, Appendix E.2.3). IL-
pretreated samples showed significantly greater (P<.005) released glucose and xylose
concentration than all other pretreated samples (Appendix G1 and G2). It was also
observed that the enzymatic hydrolysis of IL-pretreated sample was quite fast and it
released 3.3 mg/ml of glucose within 3 h after the start of hydrolysis.
(a). Cellulose Digestibility (%)
It was determined that the glucose release from IL-pretreated sample was more rapid;
therefore, the cellulose digestibility after 3 h of enzymatic hydrolysis was determined.
The cellulose digestibility of 79.8% was determined after 3 h; however, for the
untreated control and water treated control the digestibility (%) after 3 h was noted as
15.6% and 8.09%, respectively. The hydrolytic process was completed after 72 h and
cellulose digestibility of 11.3, 19.3 and 97.4% was determined from hydrolysis of the
untreated control, water treated control and IL-pretreated bagasse sample (Fig 4.20.a,
Appendix E2.2).
(b). Xylan Digestibility (%)
Xylan digestibility of IL pretreated sample was reported as 65.1% after 3 h, whereas
for water treated sample at 110ºC and untreated bagasse sample, the xylan
digestibility percentages were noted as only 4.2 and 0.1 % respectively (Fig 4.20.b,
Appendix E.2.4). The hydrolytic process completed at 72 h and hemicellulose
digestion was determined as 98.6% from IL pretreated bagasse while 8.3% and 1.4%
respectively hemicellulose digestibility was noted from water treated control and
untreated control samples respectively. Enzymatic hydrolysis results clearly showed
that soluble sugars were released faster to a greater extent when an IL pretreatment of
sugarcane bagasse was used rather than the autohydrolysis pretreatment. It was also
observed that total processing time to reach 60% cellulose digestibility was about 48 h
with autohydrolysis but it was reached up to 79.8% within 3 h with IL pretreatment.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 110
Fig. 4.19.a. Glucose concentration released from IL pretreated samples during
enzymatic hydrolysis
Fig.4.19.b. Xylose concentration released from IL pretreated samples during
enzymatic hydrolysis
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
0 24 48 72Glu
cose
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mg/
ml)
Time (hrs) Untreated Control
Water-treated control (110 C-30 min)
IL-treated control (110 C-30 min)
0
0.2
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0.8
1
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1.4
1.6
0 10 20 30 40 50 60 70 80
Xyl
ose
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nce
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n (
mg/
ml)
Time (hrs) Untreated Control
Water-treated control (110 C-30 min)
IL-treated control (110C-30 min)
PhD Thesis
Enhanced production of biofuel from sugar industry waste 111
Fig. 4.20 (a): Cellulose digestibility from IL pretreated samples during enzymatic
hydrolysis
Fig. 4.20 (b): Xylan digestibility from IL pretreated samples during enzymatic
hydrolysis
0
10
20
30
40
50
60
70
80
90
100
0 12 24 36 48 60 72
Ce
llulo
se D
ige
stib
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(%
)
Time (hrs)
Untreated Control
Water-treated control (110 C-30 min)
IL-treated control (110 C-30 min)
0
20
40
60
80
100
120
0 10 20 30 40 50 60 70 80
Xyl
an d
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(%)
Time (hrs) Untreated Control
Water treated control
IL treated
PhD Thesis
Enhanced production of biofuel from sugar industry waste 112
FERMENTATION
Ethanol production from fermentation of pretreated/enzymatically deconstructed
samples of sugarcane bagasse showed that different microbial strains have different
abilities to produce ethanol from the available sugars.
(i). Autohydrolyzed Bagasse
Ethanol production obtained from bagasse autohydrolyzed at 190ºC for 10 min was
66.02 mg/g-substrate when it was fermented with S. cerevisiae (Lalvin EC-118);
whereas, bagasse pretreated at 205ºC showed maximum ethanol production (70.9
mg/g-substrate) when S. cerevisiae (MZ-4) was used as fermenting organism. Only
15.5 mg/g-ethanol was released when enzymatic hydrolysis were carried out with an
untreated bagasse and then subjected to fermentation process by using MZ-4 strain
(Fig 4.21.a, Appendix E.3).
(ii) Ionic Liquid Pretreated Bagasse
Best ethanol production (78.8 mg/g-substrate) was obtained when sugarcane bagasse
was pretreated with IL ([C4mim][OAc]) at 110ºC for 30 min and fermented with S.
cerevisiae (MZ-4) strain (Fig 4.21.b, Appendix E.3). This strain can be considered as
the most tolerant strain in [C4mim][OAc] pretreatment conditions and played
important role in production of maximum ethanol. The maximum ethanol production
obtained from water treated bagasse at 110ºC for 30 min was 28.42mg/g-substrate
when it was fermented with S. cerevisiae (Lalvin EC-118). Pitchia stipites was
considered as more efficient to ferment xylose into ethanol but it showed less
production with all pretreated samples. During fermentation process, IL-pretreated
samples showed significantly greater (P<0.05) production of ethanol than all
pretreatment strategies; however, significance was not observed between IL-
pretreated and samples autohydrolyzed at 205°C (Appendix G3).
PhD Thesis
Enhanced production of biofuel from sugar industry waste 113
Fig.4.21: Production of Bioethanol from untreated, autohydrolyzed and IL pretreated
sugarcane bagasse
0
10
20
30
40
50
60
70
80
90
Untreatedcontrol
Water treatedcontrol 110 C
Ionic liquid110C
Autohydrolysis190 C
Autohydrolysis205 C
Eth
ano
l (m
g/g-
sub
stra
te)
Pretreatment Strategies
Uvaferm-43 Lalvin EC-118 MZ-4 Pitchia stipilis
PhD Thesis
Enhanced production of biofuel from sugar industry waste 114
Chapter 05
Discussion
PhD Thesis
Enhanced production of biofuel from sugar industry waste 115
Bioethanol is a type of liquid fuel which can easily be produced from sugar rich
materials and mainly used in substituent to gasoline. The main focus of this study was
to enhance the production of bioethanol from sugar industry waste. There were two
main types of sugar industry wastes that were utilized in this study for the bioethanol
production i.e. sugarcane molasses and sugarcane bagasse. Various fermenting yeasts
were tested under optimized physicochemical parameters and various pretreatment
strategies were employed (specifically for sugarcane bagasse) to determine more
effective conditions and microbial strain which are required to enhance the bioethanol
yield from sugar industry waste.
PART A: BIOFUEL PRODUCTION FROM SUGARCANE MOLASSES
5.1. Physicochemical Analysis of Sugarcane Molasses
The physicochemical properties of molasses vary along with the source and type of
molasses. During current study, various physicochemical properties i.e. sugar content,
brix, specific gravity was determined. Curtin et al., (1983) suggested that the large
variation in total sugar or carbohydrate content was observed in molasses from
various sources and types. The sugar content of molasses in current study was
determined as 49% with 15% reducing and 32.3% non-reducing sugar. Previously it
was believed that the sugar mill could control the sucrose content depending up on the
production technology employed by the sugar industry. It was also observed that the
centrifugation process which helped in separation of sugar and water played an
important role in determining the content of sugar present in molasses (Curtin et al.,
1983). The term brix was originated for a pure sugar (specifically sucrose) solution;
however, for the molasses this term is used for total solid content due to the presence
of various types of sugars i.e. fructose, glucose, raffinose and many non- sugar
organic contents (Curtin, 1983). The brix of molasses during current research was
noted as 79 °brix. Curtin et al., (1983) suggested that the term brix only represent a
number related to specific gravity rather than dry matter content or sucrose. Specific
gravity can be defined as the ratio of the density of a substance to the density of
reference material i.e. water. In current study, the specific gravity was noted with the
help of gravity hydrometer and was found 1.40; however, in some previous studies,
the specific gravity was determined as 1.43 for a test molasses (Olbrich, 1963).
PhD Thesis
Enhanced production of biofuel from sugar industry waste 116
5.2. Isolation, Screening and Characterization of Indigenous Yeast
During pioneer studies on fruit ecology, the majority of yeasts were isolated from
fresh grapes (Fleet et al., 2002). In our current study, the isolation of yeast strains was
carried out from various fruits and soil samples. Twenty five yeast strains were
isolated and screened for the ethanol tolerance, and one of the strains, which was
isolated from grapes showed maximum of 15% (v/v) ethanol tolerance and labeled as
MZ-4. Strain MZ-4 was identified through morphological and molecular methods
which showed 100% resemblance with S. cerevisiae strain S288C. Previously Li et
al., (2010) worked on varieties of the yeasts associated with grapes. The yeast strains
identified in grapes were Sporidiobolus pararoseus, Cryptococcus carnescens,
Cryptococcus flavescens, Candida inconpicua, Candida quercitrusa, Cryptococcus
magnus, Hanseniaspora guilliermondii and Zygosaccharomyces fermentat. Various
studies on grapes microbial ecology showed that the most common yeast found in
healthy grapes were Saccharomyces cerevisiae (Fleet et al., 2002; Barata et al., 2012).
Cabrera et al., (1988) worked on five different yeast strains and the best yeast for the
production of ethanol was determined as S. cerevisiae (Cabrera et al., 1988).
Different types of yeast strains showed variation in their ethanol tolerance ability, and
their intolerance against high concentration of ethanol affect the productivity of the
bioethanol (Lam et al., 2014). In present study, MZ-4 strain was tolerant up to 15%
ethanol; therefore, this strain was selected for further experimentations to enhance the
production of bioethanol. The increase in ethanol tolerance among various strains can
be attributed to the increase in proportion of unsaturated fatty acids, ergosterol and the
biosynthesis of phospholipids with in cytosol and membrane structures. It was
suggested that the decrease in sterol, protein ratio and phospholipids enhanced the
plasma membrane fluidity, thus adversely affected the ethanol tolerance of microbial
strain (Alexandre et al., 1994; Dinh et al., 2008). Basso et al., (2011) reported that the
increase in ethanol content in fermentation medium might decrease the number of
living cells by affecting their enzyme activity and growth of fermenting microbe
which in turn reduced the final ethanol yield.
5.3. Comparison of Commercial Strains with Indigenous Strain MZ-4
In order to compare the newly isolated strain MZ-4 with the best available
commercial strains, four commercial strains were selected i.e. Rossmoor, Saf-gold,
PhD Thesis
Enhanced production of biofuel from sugar industry waste 117
Uvaferm-43 and Lalvin EC-1118. Two main problems faced by fermenting microbes
were osmotic and ethanol intolerance (Basso et al., 2011); therefore, the best ethanol
tolerant and osmotic tolerant strain was selected for comparison. Ethanol tolerance for
the commercial strains from already published data was found as 6, 12, 18 and 18%
(v/v) respectively (Bechem et al., 2007; Schmidt et al., 2011; Sultana et al., 2013).
For the selection of most efficient strain, osmotic tolerance of all the commercial
strains and indigenous MZ-4 strain was also determined. MZ-4 showed the best
osmotic tolerance among all the five strains and Lalvin EC-1118 was the most
efficient among industrial strains only. Lalvin EC-1118 and MZ-4 showed best
ethanol production of 9.6 and 10.1% (v/v) respectively in the presence of 25% (w/v)
sugar in molasses dilutions. It was observed that the increase of sugar concentration in
fermentation medium had positive effect on increase of ethanol production. However,
there was certain limit up to which any strain could tolerate the sugar concentrations,
beyond which the ethanol yield started decreasing. These findings justified a previous
study which revealed that the increase in sugar concentration enhanced the production
of ethanol up to 5.3% (w/v) from 30% (w/v) of the sugar concentration in
fermentation medium (Periyasamy et al., 2009). Arshad et al., (2008) during his study
determined the production of 7.7% (v/v) of ethanol in presence of 16% (w/v) sugar in
the fermentation medium. Many previous studies reported that 15% (w/v) was the
optimum sugar concentration for the maximum production of bioethanol (Amutha and
Gunasekaran, 2001; Alegre et al., 2003; Mariam et al., 2009).
The determination of fermentation efficiency at different sugar concentration revealed
that, yeast strains were not able to utilize sugar completely (i.e. 100% fermentation
efficiency) at increased sugar concentration. It was observed, at 25% (w/v) of sugar
concentration, Lalvin EC-1118 and MZ-4 strain converted sugar in to bioethanol up to
60 and 63.1% (w/v), respectively. This study confirms the previous studies that
showed the decrease in fermentation efficiency with an increase in sugar
concentration. Fadel et al., (2013) and Nofemele et al., (2012) reported 75% and 76%
of fermentation efficiency with actual ethanol yields of 8.4 and 7.6% (v/v)
respectively.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 118
Two strains i.e. Lalvin EC-1118 (commercial strain) and MZ-4 (indigenous strain)
were selected on the basis of their best ethanol and osmotic tolerance and the
physicochemical conditions of both strains were optimized to determine the maximum
ethanol could be produced by these strains. The effect of pH on fermentation process
was discussed by Methewson et al., (1980) during his study that slightly low pH not
only promote the growth of fermenting yeast, but also retard the growth of
contaminating lactic acid bacteria. During current study, the effect of pH on enhanced
production of bioethanol was studied which showed that pH 4.5 and 5.0 were best for
the strains Lalvin EC-1118 and MZ-4, respectively. The optimum pH of both strain
lies between the range 4.0 to 5.0 as already suggested in previous studies (Patrascu et
al., 2009; Periyasamy et al., 2009; Mukhtar et al., 2010). In various studies, it was
observed that the increase in pH of fermentation medium degraded the ethanol into
various organic acids and glycerol, thus reduced the ethanol production; however, the
increase of pH up to 7.0 enhanced the production of glycerol and increased the
activity of aldehyde dehydrogenase enzyme which favored the conversion of
acetaldehyde in to acetic acid, thus reduced the production of bioethanol (Wang et al.,
2001).
It has been widely studied that the temperature has crucial effect on yeast growth and
fermentation process (Laluce et al., 1993; Phisalaphong et al., 2006; Periyasamy et
al., 2009). In current study, the effect of temperature on both strains was studied to
determine their optimum temperature and it was observed that Lalvin EC-1118 and
MZ-4 showed maximum ethanol production at 30 and 33°C, respectively. The
previous studies on ethanol production from S. cerevisiae also indicated that the best
temperature for the yeast growth and production of bioethanol ranges 30 to 35°C
(Periyasamy et al., 2009; Mukhtar et al., 2010). Different studies revealed that the
increase in temperature exhibited adverse effect on enzyme’s catalytic activity, and at
very high temperature cellular proteins were disrupted and denatured which affected
the growth of yeast cells structures (Mariam et al., 2009; Dhaliwal et al., 2011;
Nofemele et al., 2012).
The effect of inoculum size and age on production of bioethanol was also determined
in current study, and it was observed that the strain Lalvin EC-1118 and MZ-4
produced maximum of ethanol when 7.5 and 10% (v/v) of 24 h old culture
PhD Thesis
Enhanced production of biofuel from sugar industry waste 119
(containing 3x108
live cells per ml) were inoculated, respectively. These results
confirmed the findings of previous researches demonstrating that the inoculum size
and age directly affect final ethanol yield. It was determined by Munene et al., (2002)
that the inoculum size of 7×106 viable count/ml yielded maximum ethanol with
minimum byproducts i.e. glycerol. Similar observations were reported by Laopaiboon
et al., (2007) that 1x108
cells/ml was the optimized inoculum size for maximum
ethanol production. Later, Perisyasmi et al., (2009) during his study on S. cerevisiae
revealed that 2 g of yeast inoculum exhibited maximum production of bioethanol.
Further studies carried by Benerji et al., (2010) determined that 1.5% (v/v) of 48 h old
inoculum was best for the maximum production of bioethanol.
During early times, it was considered that the fermentation process is not affected by
the addition of nitrogen source; however, with the advent of researches it was found
that the efficiency of fermenting microbes are greatly affected by various nutrient
supplements (Casey et al., 1983). The majority of researchers, who studied the effect
of nitrogen sources on the production of bioethanol, determined that the change in
amount of nitrogen in fermentation medium enhanced ethanol yield by altering the
activity of enzymes involved in fermentation (Thomas et al., 1996; Yalçin and Özbas,
2004). During current study, various nitrogenous sources i.e. urea, ammonium
chloride (NH4Cl), ammonium nitrate (NH4NO3), ammonium sulfate ((NH4)2SO4) and
di-ammonium phosphate ((NH4)2HPO4) were added in fermentation medium in range
0.0-0.15% (w/v) to compare the effectiveness of these compounds as compared to
urea. The best nitrogen source for Lalvin EC-1118 and MZ-4 was determined as 0.1%
(w/v) of (NH4)2HPO4 and NH4Cl, respectively. These results verified the effect of
various nitrogen sources reported in previous studies; however, the type and quantity
of the nitrogen source depends on fermenting strain and source of substrate.
Previously, Bafrncová et al., (1999) studied that the addition of urea as nitrogen
source played an important role to enhance the tolerance of fermenting strain against
high concentration of ethanol. Similarly, Mukhtar et al., (2008) has been studied the
effect of urea and (NH4)2HPO4 and showed enhancement of bioethanol production by
the addition of both of these nitrogenous sources. Nofemele et al., (2012) inferred
from his research that 2 g/L of urea was best to enhance the ethanol yield up to
maximum limit. Another study conducted by Maharjan et al., (2012) revealed that
PhD Thesis
Enhanced production of biofuel from sugar industry waste 120
ethanol yield increased up to 7.3 mg/ml by the addition of di-ammonium phosphate at
concentration of 1mg/ml.
The presence of various heavy metals in molasses e.g. Zn, Cu, Fe and Mn plays an
important role in growth of yeast cells but their higher concentrations can have
inhibitory effects. Due to this reason, the use of various chelating agents improves the
fermentation product by binding to toxic metals present in crude fermentation
medium (Pandey and Agarwal, 1993). During current study, various chelating agents
i.e. EDTA, K4Fe(CN)6, and NaK-Tartrate were added in to fermentation medium in
concentration range 0.0025-0.325% (w/v) to determine their effect on production of
bioethanol. It was observed that Lalvin EC-1118 and MZ-4 produced maximum
amount of ethanol in the presence of 0.04% and 0.01% (w/v) of K4Fe(CN)6,
respectively. The current study confirmed the findings reported in previous studies
that addition of chelating agents had positive effect on enhanced production of
bioethanol. Panday and Agarwal (1993) compared the effect of EDTA, K4Fe(CN)6,
and NaK-Tartrate and determined that the addition of EDTA as chelating agent at its
optimal dose i.e. 0.05 g/L showed maximum production of bioethanol. Similar results
were reported by Benerji et al., (2010), who found that addition of 1.2 g/L NaK-
Tartrate enhanced the production of bioethanol up to 12.0% (v/v). In a different study
conducted by Yadav et al., (1997) maximum production of ethanol was also observed
by the addition of 250 ppm of K4Fe(CN)6, and it reduced content of Fe from 85 to 47
ppm, and Cu from 7.3 to 5.4 ppm.
5.4. Fed Batch Fermentation
Different methods have been proposed for the production of bioethanol from
sugarcane molasses i.e. batch, fed batch and continuous fermentation (Yoshida et al.,
1973). The batch fermentation was the most common method in brewing industry for
the production of bioethanol. One of the major bottlenecks of batch fermentation is
the intolerance of fermenting microbes against high sugar concentration present in
molasses. Increase in ethanol production can be observed by using higher sugar
concentration up to certain limit, beyond which it hinders the growth of fermenting
microbes thus stopped fermentation process (Cheng et al., 2009). In present study, the
fed-batch fermentation was also employed to compare the difference in ethanol yield
by using batch or fed-batch fermentation. Fed-batch fermentation processes are
PhD Thesis
Enhanced production of biofuel from sugar industry waste 121
widely applied to reduce substrate inhibition to achieve high productivity. During fed
batch fermentation, substrate is added after regular interval to reduce its inhibitory
effect and enhance the productivity without the removal of fermentation broth (Hunag
et al., 2012). The process is more successful in terms of high ethanol yield with fast
saccharification rate, decreased substrate inhibition and process completion time
(Cheng et al., 2009). Optimization of fed batch process is quite challenging because
of some physical constrained and non-linear dynamic equations which governed the
process (Hunag et al., 2012). In present study, enhanced production of bioethanol was
studied employing fed batch fermentation while using Lalvin EC-1118 and MZ-4 as
fermenting strains. The results of fed-batch fermentation were quite interesting as
compared to batch fermentation. It was observed that Lalvin EC-1118 strain produced
13.9% (v/v) of ethanol at 1.090 sp. grv. (17% (w/v) sugar) when molasses was fed
after every 12 h, whereas MZ-4 strain produced maximum ethanol of 13.5% (v/v) at
same sugar concentration but the optimum feeding time for this strain was 24 h. It was
observed during the study that more delay in feeding time and higher initial specific
gravity also reduced the final ethanol production. The reduction in ethanol yield with
increased specific gravity of molasses can be attributed to high osmotic pressure
created in fermentation medium with increase in sugar concentration which affected
the growth of yeast cells and also fermentation process (Cheng et al., 2009). Roukas
et al. (1991) illustrated that the increase in sugar concentration can cause plasmolysis
by decreasing water activity, thus reduced the rate of fermentation. In previous
studies, Laopaiboon et al., (2007) has been reported 120 g/L of ethanol obtained after
fed batch fermentations. Hunag et al., (2012) worked to optimize feeding rate, feeding
time, feeding glucose of a fed batch fermentation process which depicted an enhanced
productivity by 4.4%. Similarly, Bideaux et al. (2006) has been shown that high
performance fed batch fermentation enhanced the ethanol yield up to 0.34 g/g when
700 g/L of glucose solution was fed to fermenter and also helped in minimizing the
glycerol production during the process.
The comparison of fermentation efficiency showed that the fermentation efficiency of
the process increased to 81.1% when Lalvin EC-1118 strain was used for
fermentation; however, in case of MZ-4 the fermentation efficiency was increased to
83.2%. An increase in fermentation efficiency during fed batch fermentation showed
that the step wise addition of molasses helped microbes to avoid the problems of
PhD Thesis
Enhanced production of biofuel from sugar industry waste 122
osmotic intolerance, and it efficiently converted majority of available sugar into
bioethanol. In comparison, MZ-4 showed better fermentation than Lalvin EC-1118
strain which can be beneficial in terms of utilizing maximum of sugar to enhance
production of bioethanol. Li et al., (2012) showed an increase in fermentation
efficiency up to 90% by employing fed batch fermentation using E. coli as fermenting
microbe.
During evaluation of process completion time, it was noticed that the time required to
complete fed batch fermentation by using Lalvin EC-1118 and MZ-4 strain under
optimized condition was 86 h and 120 h, respectively. The industries which are more
concerned with time constraints and distillation cost should prefer Lalvin EC-1118
strain over MZ-4 because it showed rapid conversion of sugar in to bioethanol and
also ethanol concentration was much higher in case of utilizing former strain. In
contrast, those industries, which are much concerned about their fermentation
efficiency and prefer to convert maximum of the sugar into bioethanol should prefer
MZ-4 strain because of its better fermentation efficiency.
In Pakistan, the previous research on enhanced production of bioethanol by
employing fed batch fermentation was carried out by Mukhtar et al., (2009) and he
determined the production of 8.3% (v/v) of bioethanol under optimized condition.
During current study, it was observed that the optimization of process enhanced the
ethanol production up to 10% (v/v); whereas the process shifting to fed-batch
fermentation utilizing same microbial strains enhanced the ethanol production up to
13.9%. Moreover, the fed batch fermentation process enhanced fermentation
efficiency and reduced process completion time. Therefore, it can be suggested that
fed batch fermentation is more efficient and economic process as compared to batch
fermentation and it should be adopted by sugar industries in Pakistan to get more
economic benefit.
PART B: BIOFUEL PRODUCTION FROM SUGARCANE BAGASSE
5.5. Pretreatments of Sugarcane
This study investigated various pretreatment strategies i.e. autohydrolysis and IL
([C4mim][OAc]) pretreatment of sugarcane bagasse, and comparatively evaluated
PhD Thesis
Enhanced production of biofuel from sugar industry waste 123
more appropriate technique to increase enzymatic digestibility and bioethanol
production. Studies on various alkylimidazolium salts reveal that shorter alkyl chain
of [C2mim]+ imparts greater extent of saccharification with faster dissolution.
However, higher dissolution extent of [C2mim]+ does not benefit overall process of
pretreatment since losses in [C4mim]+-treated biomass were much less as compared to
[C2mim]+ pretreatment process. In terms of hemicellulose saccharification yield,
[C4mim]+ ILs perform better as hemicellulose is preserved in its polymeric and
recovered form after pretreatment (Karatzos et al., 2012). Due to these reasons,
[C4mim][OAc] (1- butyl-3-methyl imidazolium acetate) pretreatment was selected for
this study and compared with high temperature autohydrolysis.
5.6. Compositional Analysis of Sugarcane Bagasse
The chemical composition of untreated sugarcane bagasse was 37.7% glucan, 18.5%
xylan and 31.9% lignin that were comparable to previous reports (Pitarelo, 2007; Qiu
et al., 2012; Batalha et al., 2015). During autohydrolysis, hemicelluloses were
converted into soluble oligomers and monomers which degraded the intact
lignocellulosic structure. The release of hemicellulose also accompanied with partial
release of lignin fraction (mainly acid soluble lignin) (Lee et al., 2009). Comparative
to ionic liquids, autohydrolysis has shown more promising effect on dissolution of
hemicelluloses. It was inferred from the results that maximum xylan dissolution was
observed when autohydrolysis was carried out at high temperature condition i.e.
205ºC for 6 min. In comparison to autohydrolysis, ionic liquid exhibited less effect on
dissolution of hemicelluloses. Since hemicellulose forms a physical barrier which
prevents compact cellulose structure from enzymatic attack; autohydrolysis has been
considered as a good method to remove this barrier, thereby increasing enzymatic
cellulose digestion. Other studies also indicated that the degree of xylan dissolution
depends on severity of pretreatment condition (Boussarsar et al., 2009).
A significant increase in lignin content was observed in biomass after autohydrolysis
which might be attributed to the removal of significant amount of hemicellulose and
certain amount of cellulose while retaining most of the lignin (Qiu et al., 2012;
Vallejos et al., 2012; HU, 2014). Some researchers suggested that the increased lignin
content might be due to the repolymerization of polysaccharides degradation product
(such as furfural) and/or polymerization with lignin, which forms a lignin like
PhD Thesis
Enhanced production of biofuel from sugar industry waste 124
material termed as pseudo-lignin (Li et al., 2007). The pseudo-lignin can also be
generated from carbohydrate without significant contribution from lignin, especially
under high severity pretreatment conditions (Sannigrahi et al., 2011). Previous
researches have shown that the major impacts of autohydrolysis on lignin were its
translocations and redistributions, resulting in formation of lignin droplets of various
morphologies on cell wall. The pretreatment that exceed critical phase transition
temperature of lignin allow it to expand and migrate to larger void, where it is
reshaped by aqueous environment into spherical droplet (Donohoe et al., 2008).
Lignin droplet can leave the cell matrix, move into solution and are relocated to the
surface of biomass. In addition, some of the dissolved lignin is re-precipitated onto
the surface of biomass, especially in a batch reactor, as the system is cooled (Jung et
al., 2010; HU, 2014; Pu et al., 2015).
During our current studies, the IL pretreatment lead to greater dissolution and removal
of lignin in bagasse than what was accomplished under comparable autohydrolysis
conditions. The dark brown color of the IL-treated sample, just after the onset of
reaction, showed its excellent ability to extract lignin from bagasse (Sant'Ana da Silva
et al., 2011). It has been previously reported that the ionic liquid cation interacts with
lignin through Π-Π interaction to help in lignin dissolution; however, complete
dissolution of lignin was difficult due to location of lignin within lignin–carbohydrate
complex and hydrophobicity (Qiu et al., 2012). Ionic liquid exhibited better effect on
lignin dissolution as compared to autohydrolysis thus assisting in enzymatic
accessibility but both pretreatment methods has limited effect on cellulose removal
because of its highly packed crystalline structures which are resistant to high
temperature (Qiu et al., 2012; Vallejos et al., 2012; Qiu and Aita, 2013). The increase
in cellulose content after autohydrolysis was attributed to the significant removal of
hemicelluloses. The effect of both pretreatments on lignocellulosics conversion was
further studied by FTIR and XRD analysis.
5.7. Structural Analysis of Sugarcane Bagasse
Attenuated total reflection-Fourier transform infrared spectroscopy (ATR–FTIR) of
untreated and pretreated bagasse was carried out. Previous studies showed that the
peaks at 3175-3490 cm-1
showed O-H stretching intra-molecular hydrogen bonds for
cellulose I (Kumar et al., 2014; Poletto et al., 2014; Sun et al., 2014). In present
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Enhanced production of biofuel from sugar industry waste 125
study, a reduction of this peak in autohydrolyzed samples showed the effectiveness of
severity on OH-stretching molecules. The band intensity at 3336 cm-1
after water
treated sample at 110°C represented cellulose hydrogen bonding and possible co-
crystallization due to pretreatment; however, comparatively lower absorption band
was observed from [C4mim][OAc] pretreated samples at same conditions. The peaks
associated to lignin structure are 1604 and 1510 cm-1
(Adapa et al., 2011; Kumar et
al., 2014), which showed during current study a remarkable decrease in lignin content
in autohydrolyzed and IL pretreated sample; however, some of the autohydrolyzed
samples showed an increase in peak which might be due to removal of large amount
of hemicelluloses which in turn increased the lignin content. Similar results were
reported by Kartoz et al., (2012) who demonstrated that the bagasse treated with
[C2mim][OAc] showed reduction in these peaks as compared to untreated bagasse.
During compositional analysis, an increase in lignin content was observed due to
removal of large amount of hemicellulose; however, the reduction in these specific
FTIR peaks cleared that some of the lignin structure was also removed during
pretreatment despite of its increase in overall composition. The band positions at 1730
and 1243 cm-1
are assigned to acetyl group of hemicelluloses (Adapa et al., 2011;
Kumar et al., 2014; Sun et al., 2014). During current study, the reduction in these
bands in all pretreated samples showed the removal of hemicelluloses component
from sugarcane bagasse. Similar results were found by Sun et al., (2014), which
showed the effect of various pretreatment strategies on removal of hemicellulose
associated peaks. Similarly, the reduction in peak at 1160 cm-1
was also observed
after both pretreatment during current study which was associated with hemicellulose
structure as reported by (Kumar et al., 2014). The bands associated with cellulose
structures are 1429, 1370, 1319, 1103 and 898 cm-1
(Karatzos et al., 2012; Kumar et
al., 2014). The band position at 1421 cm-1
is mainly due to CH2 scissor motion in
cellulose. In current study, the increase in band intensity at 1421 cm-1
and other
cellulose associated band can be attributed to increase in cellulose content due to
removal of lignin and hemicellulose content. During compositional analysis of
bagasse it was observed that removal of hemicellulose content resulted in increased
cellulose and lignin content. Similar results were studied by Sun et al., (2015) that the
cellulose band intensity was increased after pretreatments due to decrease in
hemicellulose content. Moreover, the present study showed that the spectra obtained
from autohydrolyzed samples showed clear peaks at 1103 cm-1
and a reduction of the
PhD Thesis
Enhanced production of biofuel from sugar industry waste 126
amorphous band at 898 cm-1
, which demonstrated an increase in crystallinity. The
peak at 1103 cm-1
(referring to crystalline cellulose) was diminished after IL
pretreatment which is a clear indication of cellulose crystallinity. Similar results were
found in previous studies where various pretreatment strategies reduced crystallinity
after IL pretreatment as reported by Li et al., (2010); however, Sun et al., (2015)
reported an increase in crystallinity after acidic pretreatment. These results clearly
demonstrated that how both pretreatments effectively weaken the van der Waals
interaction between cell wall polymers (Li et al., 2010).
5.8.Crystallinity Measurement
The quantitative analysis of absorption spectrometry is based on the Beer-Bouguer-
Lambert law which implies that absorption band intensities are linearly proportional
to the concentration of each component (Adapa et al., 2011). During this research the
peak heights were used as quantitative parameter as stated by Adapa et al. (2011), and
the heights of the peaks were determined by measuring the difference between
maximum peak intensity and baseline (Adapa et al., 2011). Total crystallinity index
(TCI) and Lateral order index (LOI) was determined for all pretreated samples. The
term Lateral order index (LOI) was assigned to two ratios related to cellulose
structure were calculated i.e. 1424 cm-1
/898 cm-1
(Hurtubise and Krässig, 1960;
Spiridon et al., 2011; Qiu et al., 2012). It has been used by many previous researchers
to show the presence of cellulose I structure in cellulose material (Oh et al., 2005;
Spiridon et al., 2011). Total crystallinity index (TCI) was the term used by Nelson
and O’Connor (1964) for the ratio of 1371 cm-1
/2919 cm-1
, and used by various
researchers to evaluate the infrared crystallinity (IR) ratio (Nelson and O'Connor,
1964; Spiridon et al., 2011; Qiu et al., 2012). Thus, the higher values of both LOI and
TCI are indicative of the more ordered structure of cellulose and higher crystallinity
of biomass (Qiu et al., 2012). The order of crystallinity determined by LOI was 205ºC
> 190ºC > untreated bagasse > 110ºC > IL pretreated bagasse which also corroborated
with the CrI (crystallinity index) determined by XRD analysis. The TCI values of
different pretreated samples showed deviation from this order which can be attributed
to hydrocarbonate linear chain extractives which can be associated with 2900 cm-1
band intensity (Ornaghi et al., 2014), thus showed higher values in this specific band,
PhD Thesis
Enhanced production of biofuel from sugar industry waste 127
decreasing the calculated total crystallinity value (Ornaghi et al., 2014; Poletto et al.,
2014). However, the evaluation of LOI was based on 898 cm-1
band, which is
associated with amorphous cellulose, so a higher intensity in this band indicates more
amorphous content (Ornaghi et al., 2014). These reduction in values showed that
during IL pretreatment process, crystalline structure of cellulose was converted into
amorphous cellulose (Li et al., 2010). Similar results were found by Spiridon et al.,
(2010) that the IL pretreatment reduced the crystallinity of cellulose as determined by
TCI and LOI thus it provided more surface area for enzyme attachment and
conversion. Qiu et al., (2012) pretreated the bagasse with [C2mim][OAC] which was
shown to have positive effect on reduction of crystallinity determined by measuring
TCI and LOI. Zhu et al., (2012) showed that LOI and TCI of sugarcane bagasse was
decreased when treated with NH4OH–H2O2+[Amim]Cl-pretreated (100°C for 1 h),
similarly, Kuo et al. (2009) also observed the decrease in TCI and LOI values when
sugarcane bagasse was treated with N-methylmorpholine-N-oxide (NMMO) at 100°C
for 7 h.
XRD analysis was performed to examine the cellulose crystallinity index of biomass
(Park et al., 2010). The slight increase in CrI in autohydrolyzed samples can be
attributed to removal of amorphous region i.e. hemicellulose, lignin or amorphous
cellulose and rearrangement of remaining components (Ruiz et al., 2011; Zhang et al.,
2012). Lei et al., (2013) reported that the dilute acid pretreatment was unable to break
cellulose hydrogen bonding but removed the amorphous components; thus increased
the crystallinity of biomass. The reduction in CrI of IL treated sample was observed,
which exhibited reduction in cellulose crystallinity in bagasse sample treated with
[C4mim][OAc]. Previous studies has been showed the crystallinity index of untreated
bagasse as 0.56 which was reduced to 0.24 after [C2mim][OAc] pretreatment (Qiu et
al., 2012). Li et al., (2010) and Saliva et al., (2011) also determined the reduction in
CrI after pretreatment of biomass with [C2mim][OAc]. It was suggested that anion
and cation in IL were responsible for disruption of cellulose structure. The cation
interacted with lignin though Π-Π interaction and hydrogen bonding whereas anionic
acetate acted as hydrogen bond acceptor that attacked the free hydroxyl group of
cellulose and deprotonated it, thus reduced cellulose crystallinity (Qiu and Aita, 2013;
Ninomiya et al., 2015). Hydrogen bonding in cellulose structure was disrupted and
replaced by another hydrogen bonding between cellulose hydroxyl and anions of ionic
PhD Thesis
Enhanced production of biofuel from sugar industry waste 128
liquid, thus it caused disruption and dissolution of cellulose structure and reduced its
crystallinity (Qiu and Aita, 2013).
5.9.Enzymatic Hydrolysis
The cellulose digestibility is considered as an important factor to select the most
efficient method of pretreatment. Some important factors which act as a barrier during
enzymatic hydrolysis of a biomass are lignin hindrance, hemicellulose content,
porosity, cellulose degree of polymerization and cellulose crystallinity. Variation in
glucose and xylose concentration released by enzymatic hydrolysis of sugarcane
bagasse pretreated with different strategies was observed and the major effect found
by autohydrolysis on lignocellulosic material was removal of hemicellulose which
increased the accessibility of enzymes to cellulosic content, thus higher concentration
of sugars were obtained with increase in pretreatment temperature (C. Li et al., 2010;
Batalha et al., 2015). Severity in pretreatment conditions showed profound effects on
enzymatic hydrolysis. It was observed that increased pretreatment temperature of
autohydrolysis enhanced glucose release after enzymatic hydrolysis but xylose
concentration was reduced because major amount of xylan has already been removed
during autohydrolysis. Among the autohydrolyzed samples, maximum glucose
concentration was obtained from the samples autohydrolyzed at 205ºC for 6 min;
whereas maximum xylose concentration under these conditions was obtained from
sample autohydrolyzed at 190°C for 10 min. The reduction in xylose concentration
released from bagasse autohydrolyzed at 205ºC could be attributed to removal of
large hemicellulose content during high temperature autohydrolysis but low xylose
concentration autohydrolyzed sample at 110ºC might be due to more lignin hindrance
(Qiu et al., 2012; Hongdan et al., 2013; Batalha et al., 2015). Enzymatic
saccharification of the ionic liquid pretreated bagasse (at 110ºC for 30 min) released
more glucose and xylose as compared to all autohydrolyzed samples which depicted
increased conversion of cellulose into glucose as compared to other pretreatments.
Ionic liquid exhibited good effect on removal of hemicellulose but compositional
analysis and FTIR data of pretreated bagasse revealed that the effect of ionic liquid on
hemicellulose was much lesser than autohydrolysis, thus released more xylose from
biomass after enzymatic hydrolysis.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 129
Autohydrolysis was compared with ionic liquid pretreatment to determine kinetics of
enzymatic hydrolysis and cellulose digestibility, which showed increased kinetics i.e.
97.4% in IL-treated bagasse. Biomass pretreated with [C2mim][OAc] has been shown
cellulose digestibility up to 87% and 96% within 24 h of hydrolysis in various
previous studies (Li et al., 2010; Qiu et al., 2012). In case of autohydrolysis, the
limited enzymatic hydrolysis and cellulose digestibility can be attributed to
unmodified crystalline cellulosic structure. The loss in inter- and intra- molecular
hydrogen bonding during IL pretreatment resulted in amorphous cellulose and
provided an enhanced surface area leading to better enzyme accessibility and
increased binding sites in recovered cellulose fibers (Li et al., 2010; Qiu et al., 2012).
Higher hemicellulose digestibility from ionic liquid pretreated bagasse might be
attributed to minimal loss of initial xylan and delignification. Silva et al., (2011)
reported 75% xylan digestion when treated with [C2mim][OAc]. In autohydrolyzed
bagasse hemicellulose were not accessible to enzymes because most of the
hemicellulose was already been removed and rest of it was covalently linked with
lignin component (Karatzos et al., 2012).
Hydrolysis results clearly showed that soluble sugars released faster to a greater
extend in IL pretreated sugarcane bagasse than autohydrolysis pretreatment. However,
reduction in enzymatic loading, low cost ionic liquid and recovery of ionic liquid are
essential to promote the economy of bio-refineries and develop the optimal ionic
pretreatment (Li et al., 2010). It was also observed that total processing time to reach
60% cellulose digestibility was about 48 h with autohydrolysis but it was reached up
to 80% within 3 h with ionic liquid pretreatment. In comparison to autohydrolysis,
ionic liquid required low energy consumption, less processing time, lead to higher
glucose yield and it is convenient and environment friendly too. These advantages are
paramount in order to counterbalance higher costs associated with ionic liquids but it
also offers motivation to explore and develop this pretreatment technique in the
future.
5.10. Fermentation
Ethanol production from fermentation of pretreated samples of sugarcane bagasse
showed that different microbial strains have different abilities to produce ethanol from
PhD Thesis
Enhanced production of biofuel from sugar industry waste 130
available sugar. The maximum amount of ethanol was obtained from IL pretreated
sample when it was fermented with newly isolated MZ-4 strain. The difference in
ethanol production amount by different strains can be attributed to their difference in
tolerance against side products released during different pretreatment conditions
(Iwaki et al., 2013). Previously, it was reported that ILs have negative affect on
growth of microorganisms; and the toxic role of ILs on microbes can be attributed to
either cationic or anionic moiety (Frade and Afonso, 2010; Pham et al., 2010).
Presence of [C2mim][OAc] (up to 1% concentration ) in fermentation medium
improves the growth of S. cerevisiae and also increases ethanol production but its
higher concentrations has negative impact on yeast growth and fermentation process
(Ouellet et al., 2011; Mehmood et al., 2015). S. cerevisiae has the ability to utilize
both monomeric sugar and sucrose which make it an efficient microbe to be used in
variety of substrates (Badotti et al., 2008; Canilha et al., 2012). Other advantages
related to its use are its highest resistance against high ethanol concentration, inhibitor
resistance and its ability to consume significant amount of substrate in adverse
conditions. Unfortunately, S. cerevisiae lacks genes which could make it able to
assimilate xylose; however, to obtain optimal ethanol yields, conversion of
hemicellulose fraction is also essential (Canilha et al., 2012). Pitchia stipites is
considered as more efficient to ferment xylose into ethanol but its less production
with all pretreated samples can be attributed to its less efficient glucose utilization as
compared to S. cerevisiae (Krahulec et al., 2012). Moreover, it was also suggested in
previous studies that all symporters in P. stipites are competitively inhibited by
glucose molecules which makes it difficult to utilize both sugars simultaneously and
hinders the conversion of xylose into ethanol (Farwick et al., 2014).
PhD Thesis
Enhanced production of biofuel from sugar industry waste 131
Conclusions
In this study, different strategies were applied to enhance bioethanol yield from sugar
industry waste under optimal physicochemical conditions. The following findings were
concluded from the study:
For the production of bioethanol from sugarcane molasses by using batch
fermentation, a newly isolated strain MZ-4 was determined as the most efficient
strain in terms of bioethanol yield and fermentation efficiency.
In comparison, fed-batch fermentation process showed better yield and
fermentation efficiency as compared to batch fermentation.
During fed batch fermentation of sugarcane molasses, Lalvin EC-1118 showed
better bioethanol production than MZ-4 in terms of actual yield; however, MZ-4
strain showed less yield with improved fermentation efficiency. Therefore,
despite of lower ethanol yield, MZ-4 can be considered as a better strain in terms
of maximum sugar conversion in to bioethanol. Lalvin EC-1118 can be preferred
for maximum yield and to avoid time constraints, because more time is required
by strain MZ-4 to complete the fermentation process.
For the conversion of sugarcane bagasse into bioethanol, IL pretreatment showed
better effect on release of sugars as compared to high severity autohydrolysis
pretreatment, which can contribute in reduction of operational cost. Similarly, the
higher cellulose and xylan digestibility was also observed after IL pretreatment,
which might be attributed to removal of lignin and hemicelluloses along with
conversion of cellulose crystalline structure into amorphous, during pretreatment.
The reaction rate for the enzymatic hydrolysis was much faster for the IL
pretreated bagasse as compared to autohydrolyzed bagasse, which makes IL
pretreatment more favorable.
In comparison to autohydrolysis, the greater ethanol production was obtained
from IL pretreated bagasse, when it was fermented with strain MZ-4.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 131
Future Prospects
A lot of work has already been done regarding production of bioethanol from yeast by
using cheaper substrates. However, still there are many problems to face while scaling up
the ethanol production in industrial scale.
Work on continuous fermentation should be done to overcome the inhibitory effect of
end product.
Genetically modified crops containing high sugar content can be used to enhance the
bioethanol production.
An effort to create genetically modified microorganisms (GMOs) to get higher
ethanol yield should be done, but they should have to certify as ―GRAS‖ (generally
recognized as safe) prior to use.
The process of simultaneous saccharification and co-fermentation should be tested on
IL pretreated bagasse by using those GMOs, which should be able to convert glucose
and xylose simultaneously.
Optimization of IL pretreatment and following fermentation process should be done
to enhance the production of ethanol.
Other pretreatment strategies on sugarcane bagasse should be tested to increase the
amount of released sugar.
Inhibitors released during this pretreatment should be determined and efforts should
be made to avoid their effects on biological processes.
This study should be scaled up and optimized to the pilot scale, so that best
determined strategies could be utilized on industrial scale at later stages.
PhD Thesis
Enhanced production of biofuel from sugar industry waste 132
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PhD Thesis
Enhanced production of biofuel from sugar industry waste 133
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Annexes
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Appendix A
A1: The Composition of WLN Media
Contents Amount (g/L)
Yeast extract 4.00
Trypton 5.00
Glucose 50.00
Potassium dihydrogen phosphate 0.55
Potassium chloride 0.425
Magnesium sulphate 0.125
Calcium chloride 0.125
Ferric chloride 0.0025
Manganese sulphate 0.0025
Bromocresol green 0.022
Agar 15.00
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Appendix B
B1: Sequence for Strain MZ-4
ccccctccgtcctgggccccagtccctccgggggcgcccttattcagtgccatccctggaggggctgaaaagcgttcccaattt
gtaatgggcggacaaaatccatactcgtgtggggggcccccattaataggtttcctggtttttgagcgtgagacgcccctattggg
agcggccccaagtgccgggtcgtccgtttgaagaaaaaaggccggaggattggggcccgctgctttttgtctagtaaatgttgca
aacaaactcagcagaagtaa
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Appendices C
C.1: Calibration curve for reducing sugar analysis by DNS method
C.2: Calibration curve for ethanol determination by HPLC method
y = 0.2682x R² = 0.9977
0
0.5
1
1.5
2
2.5
0 2 4 6 8 10
O.D
(n
m)
Reducing Sugars (mg/ml)
y = 237812x R² = 0.998
0
2000000
4000000
6000000
8000000
10000000
12000000
14000000
0 10 20 30 40 50 60
HP
LC p
eak
are
a
Ethanol % (v/v)
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C.3: Calibration curve for glucose determination by HPLC method
C.4: Calibration curve for xylose determination by HPLC method
y = 6.9543x R² = 0.9972
0
5
10
15
20
25
30
0 0.5 1 1.5 2 2.5 3 3.5 4
HP
LC p
eak
he
igh
t
Glucose Conc. (mg/ml)
y = 5.0696x R² = 0.998
0
0.5
1
1.5
2
2.5
3
3.5
4
4.5
0 0.2 0.4 0.6 0.8 1
HP
LC p
eak
he
igh
t
Xylose Conc. (mg/ml)
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C.5: Calibration curve for galactose determination by HPLC method
C.6: Calibration curve for arabinose determination by HPLC method
y = 3.1419x R² = 0.9974
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
0 0.05 0.1 0.15 0.2 0.25 0.3
HP
LC p
eak
He
igh
t
Galactose Conc. (mg/ml)
y = 57.175x R² = 0.9988
0
0.2
0.4
0.6
0.8
1
1.2
1.4
0 0.005 0.01 0.015 0.02 0.025
HP
LC p
eak
he
igh
t
Arabinose Conc. (mg/ml)
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C.7: Calibration curve for mannose determination by HPLC method
y = 48.089x R² = 0.9993
0
0.5
1
1.5
2
2.5
0 0.01 0.02 0.03 0.04 0.05
HP
LC P
eak
he
igh
t
Mannose Conc. (mg/ml)
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Appendices D
Bioethanol production from Sugarcane Molasses
D.1: Effect of pH on enhanced production of bioethanol by using Lalvin EC-
1118 and MZ-4
pH
Lalvin EC-1118 MZ-4
Ethanol
Productio
n (v/v)
S.D. Ethanol
Production
(v/v)
S.D.
3.0 6.4 ±0.124 7.2 ±0.124
3.5 7.3 ±0.081 8.2 ±0.081
4.0 9.6 ±0.163 9.6 ±0.163
4.5 9.8 ±0.081 10.1 ±0.081
5.0 8.9 ±0.163 10.2 ±0.081
5.5 8.3 ±0.081 9.5 ±0.163
6.0 8.1 ±0.081 8.2 ±0.124
S.D= Standard deviation
D.2: Effect of temperature on enhanced production of bioethanol by using
Lalvin EC-1118 and MZ-4
Temp
Lalvin EC-1118 MZ-4
Ethanol
Productio
n (v/v)
S.D. Ethanol
Production
(v/v)
S.D.
27 9.5 ±0.163 9.8 ±0.081
30 9.8 ±0.081 10.2 ±0.163
33 9.4 ±0.169 10.3 ±0.244
36 8.9 ±0.205 9.8 ±0.081
39 7.1 ±0.169 7.5 ±0.249
S.D= Standard deviation
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D.3: Effect of Inoculum size on enhanced production of bioethanol by using
Lalvin EC-1118 and MZ-4
Inoculum
Size
Lalvin EC-1118 MZ-4
Ethanol
Productio
n (v/v)
S.D. Ethanol
Production
(v/v)
S.D.
2.5 9.5 ±0.163 10.0 ±0.163
5 9.8 ±0.081 10.3 ±0.081
7.5 10 ±0.081 10.4 ±0.163
10 9.7 ±0.169 10.5 ±0.163
12.5 9.6 ±0.124 10.2 ±0.081
S.D= Standard deviation
D.4: Effect of Inoculum age on enhanced production of bioethanol by using
Lalvin EC-1118 and MZ-4
Inoculum
Age
(hours)
Lalvin EC-1118 MZ-4
Ethanol
Productio
n (v/v)
S.D. Ethanol
Production
(v/v)
S.D.
12 9.8 ±0.163 10.1 ±0.124
24 10 ±0.081 10.5 ±0.163
36 9.4 ±0.081 9.4 ±0.124
48 8.4 ±0.169 8.3 ±0.163
S.D= Standard deviation
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D.5: Effect of nitrogen sources on enhanced production of bioethanol by
using Lalvin EC-1118 and MZ-4
Nitrogen
source
Concentrati
on
Lalvin EC-1118 MZ-4
Ethanol
Productio
n (v/v)
S.D Ethanol
Product
ion (v/v)
S.D
Urea 0.05% 10.1 ±0.081 10.5 ±0.163
0.10% 10.2 ±0.163 10.7 ±0.081
0.15% 9.4 ±0.124 9.6 ±0.169
Ammonium
Chloride
0.05% 10.1 ±0.081 10.6 ±0.081
0.10% 10.3 ±0.244 10.8 ±0.081
0.15% 10.4 ±0.081 9.9 ±0.286
Ammonium
Nitrate
0.05% 10.3 ±0.081 10.5 ±0.163
0.10% 9.4 ±0.047 10.6 ±0.081
0.15% 8.9 ±0.205 10.1 ±0.081
Ammonium
Sulfate
0.05% 10.1 ±0.081 10.5 ±0.163
0.10% 10.3 ±0.163 10.6 ±0.081
0.15% 10.4 ±0.081 10.7 ±0.163
Di-ammonium
phosphate
0.05% 10.3 ±0.081 10.5 ±0.081
0.10% 10.5 ±0.081 10.6 ±0.081
0.15% 10 ±0.081 9.9 ±0.249
S.D= Standard deviation
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D.6: Effect of chelating agent sources on enhanced production of bioethanol
by using Lalvin EC-1118 and MZ-4
Chelating
agents
Conc. Lalvin EC-1118 MZ-4
Ethanol
Production
(v/v)
S.D. Ethanol
Production
(v/v)
S.D.
EDTA 0.0025 10.5 ±0.163 10.7 ±0.163
0.005 10.5 ±0.081 10.7 ±0.081
0.01 10.6 ±0.163 10.8 ±0.163
0.02 10.6 ±0.081 10.8 ±0.081
0.04 10.7 ±0.163 10.9 ±0.163
0.08 10.4 ±0.081 10.2 ±0.047
0.16 9.8 ±0.169 9.36 ±0.047
0.32 9.2 ±0.188 8.8 ±0.081
Potassium
Ferrocyanide
0.0025 10.5 ±0.163 10.7 ±0.163
0.005 10.6 ±0.163 10.9 ±0.081
0.01 10.7 ±0.081 11.1 ±0.163
0.02 10.8 ±0.081 10.3 ±0.047
0.04 10.9 ±0.163 9.7 ±0.047
0.08 10.3 ±0.094 9.1 ±0.047
0.16 9.6 ±0.124 8.5 ±0.124
0.32 9.4 ±0.081 8.0 ±0.081
Sodium
Potassium
tartrate
0.0025 10.5 ±0.163 10.7 ±0.163
0.005 10.5 ±0.081 10.7 ±0.081
0.01 10.6 ±0.081 10.8 ±0.081
0.02 10.6 ±0.163 10.8 ±0.047
0.04 10.7 ±0.081 10.1 ±0.047
0.08 10.6 ±0.124 9.2 ±0.081
0.16 10.1 ±0.162 8.4 ±0.094
0.32 10.5 ±0.163 7.7 ±0.124
S.D= Standard deviation
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Appendices E
Ethanol Production from Sugarcane Bagasse
E.1.1. Glucose concentration released from untreated and autohydrolyzed samples
during enzymatic hydrolysis
Time
(hours)
Untreated bagasse 190°C for 10 min 205°C for 6 min
Glucose
(mg/ml)
S.D. Glucose
(mg/ml)
S.D. Glucose
(mg/ml)
S.D.
0 0 ±0 0 ±0 0 0
3 0.33 ±0.027 1.05 ±0.049 1.55 ±0.015
6 0.45 ±0.045 1.35 ±0.019 2.02 ±0.075
12 0.46 ±0.039 1.55 ±0.083 2.49 ±0.088
24 0.46 ±0.014 1.88 ±0.011 2.98 ±0.067
48 0.47 ±0.014 2.20 ±0.044 3.39 ±0.067
72 0.47 ±0.014 2.37 ±0.061 3.53 ±0.148
S.D= Standard deviation
E.1.2: Cellulose digestibility of untreated and autohydrolyzed samples during
enzymatic hydrolysis
Untreated control 190190°C for 10 min 205°C for 6 min
Time
(h)
Cellulose
digestibilit
y (%)
S.D. Cellulose
digestibili
ty (%)
S.
D
Cellulose
digestibili
ty (%)
S.D.
0 0 ±0 0 ±0 0 ±0
3 8.19 ±0.675 20.85 ±0.985 27.16 ±0.278
6 10.37 ±1.109 25.43 ±0.385 34.69 ±1.328
12 11.02 ±0.962 30.62 ±1.640 42.80 ±1.550
24 11.21 ±0.689 37.08 ±0.224 51.54 ±1.179
48 11.43 ±0.344 43.55 ±0.882 58.78 ±1.190
72 11.46 ±0.344 46.93 ±1.205 60.29 ±2.602
S.D= Standard deviation
PhD Thesis
172
E.1.3: Xylose concentration released from untreated and autohydrolyzed samples
during enzymatic hydrolysis
Untreated control 190°C for 10 min 205°C for 6 min
Time
(h)
Xylose
(mg/ml)
S.D. Xylose
(mg/ml)
S.D. Xylose
(mg/ml)
S.D.
0 0 ±0 0 ±0 0 ±0
3 0.003 ±0.002 0.25 ±0.003 0.13 ±0.011
6 0.01 ±0.001 0.29 ±0.002 0.15 ±0.004
12 0.029 ±0.000 0.32 ±0.011 0.18 ±0.004
24 0.03 ±0.001 0.38 ±0.014 0.21 ±0.0057
48 0.03 ±0.001 0.41 ±0.026 0.24 ±0.0057
72 0.03 ±0.002 0.426 ±0.035 0.24 ±0.002
S.D= Standard deviation
E.1.4: Xylan digestibility of untreated and autohydrolyzed samples during
enzymatic hydrolysis
Untreated control 190°C for 10 min 205°C for 6 min
Time
(h)
Xylan
digestib
ility (%)
S.D. Xylan
digestib
ility (%)
S.D. Xylan
digestibili
ty (%)
S.D.
0 0 ±0 0 ±0 0 ±0
3 0.11 ±0.101 2.765 ±0.042 2.86 ±0.257
6 0.76 ±0.065 3.135 ±0.024 3.54 ±0.097
12 1.41 ±0.018 3.527 ±0.122 4.24 ±0.097
24 1.44 ±0.045 4.197 ±0.157 4.88 ±0.132
48 1.44 ±0.048 4.502 ±0.284 5.57 ±0.133
72 1.48 ±0.115 4.677 ±0.379 5.690 ±0.049
S.D= Standard deviation
PhD Thesis
173
E.2.1: Glucose concentration released from untreated control, water treated control
and ionic liquid pretreated samples during enzymatic hydrolysis
Untreated control A-110°C for 30 min IL 110°C for 30 min
Time Glucose
(mg/ml)
S.D. Glucose
(mg/ml)
S.D. Glucose
(mg/ml)
S.D.
0 0 ±0 0 ±0 0 ±0
3 0.33 ±0.027 0.60 ±0.192 3.31 ±0.033
6 0.45 ±0.045 0.66 ±0.018 3.64 ±0.033
12 0.46 ±0.039 0.70 ±0.001 3.67 ±0.052
24 0.46 ±0.014 0.74 ±0.016 3.77 ±0.047
48 0.47 ±0.014 0.78 ±0.016 3.92 ±0.015
72 0.47 ±0.014 0.82 ±0.004 4.04 ±0.011
S.D= Standard deviation
E.2.2: Cellulose digestibility from untreated control, water treated control and
ionic liquid pretreated samples during enzymatic hydrolysis
Untreated control A-110°C for 30 min IL 110°C for 30 min
Time Cellulose
digestibility
(%)
S.D. Cellulose
digestibility
(%)
S.D. Cellulose
digestibility
(%)
S.D.
0 0 ±0 0 ±0 0 ±0
3 8.19 ±0.675 14.25 ±0.404 79.88 ±0.800
6 10.37 ±1.109 15.61 ±0.061 87.81 ±1.273
12 11.02 ±0.962 16.54 ±0.360 88.48 ±1.133
24 11.21 ±0.689 17.46 ±0.369 90.92 ±0.362
48 11.46 ±0.344 18.48 ±0.066 94.59 ±0.276
72 11.46 ±0.344 19.31 ±0.561 97.44 ±1.476
S.D= Standard deviation
PhD Thesis
174
E.2.3: Xylose digestibility from untreated control, water treated control and ionic
liquid pretreated samples during enzymatic hydrolysis
Untreated control A-110°C for 30 min IL 110°C for 30 min
Time Xylose
(mg/ml)
S.D. Xylose
(mg/ml)
S.D. Xylose
(mg/ml)
S.D.
0 0 ±0 0 ±0 0 ±0
3 0.003 ±0.002 0.092 ±0.012 0.924 ±0.002
6 0.016 ±0.001 0.111 ±0.012 1.073 ±0.005
12 0.029 ±0.000 0.124 ±0.004 1.164 ±0.002
24 0.030 ±0.001 0.135 ±0.007 1.270 ±0.004
48 0.030 ±0.001 0.170 ±0.001 1.365 ±0.009
72 0.031 ±0.002 0.178 ±0.014 1.401 ±0.006
S.D= Standard deviation
E.2.4: Xylan digestibility from untreated control, water treated control and ionic
liquid pretreated samples during enzymatic hydrolysis
Untreated control A-110°C for 30 min IL 110°C for 30 min
Time Xylan
digestibility
(%)
S.
D
Xylan
digestibility
(%)
S.D. Xylan
digestibility
(%)
S.D.
0 0 ±0 0 ±0 0 ±0
3 0.119 ±0.101 4.280 ±0.599 65.12 ±0.198
6 0.762 ±0.065 5.170 ±0.574 75.63 ±0.399
12 1.418 ±0.014 5.800 ±0.205 81.99 ±0.187
24 1.441 ±0.048 6.320 ±0.341 89.48 ±0.318
48 1.441 ±0.048 7.911 ±0.079 96.16 ±0.684
72 1.489 ±0.115 8.321 ±0.651 98.67 ±0.476
S.D= Standard deviation
PhD Thesis
175
E.3.1: Bioethanol Production from Untreated control by various yeast strains
Strains Ethanol (mg/g-substrate) S.D.
Uvaferm-43 6.02 ±0.11
Lalvin EC-1118 12.21 ±0.25
MZ-4 15.52 ±0.05
Pitchia stipitis 10.67 ±0.11
S.D= Standard deviation
E.3.2.Bioethanol Production from bagasse autohydrolyzed at 190°C by various
yeast strains
S.D= Standard deviation
E.3.3: Bioethanol Production from bagasse autohydrolyzed at 205°C by various
yeast strains
S.D= Standard deviation
Strains Ethanol (mg/g-substrate) S.D.
Uvaferm-43 56.33 ±0.74
Lalvin EC-1118 66.02 ±0.65
MZ-4 56.86 ±0.15
Pitchia stipilis 50.09 ±1.04
Strains Ethanol (mg/g-substrate) S.D.
Uvaferm-43 68.55 ±0.75
Lalvin EC-1118 69.42 ±0.36
MZ-4 70.92 ±0.09
Pitchia stipilis 69.58 ±0.56
PhD Thesis
176
E.3.4: Bioethanol Production from bagasse autohydrolyzed at 110°C by various
yeast strains
Strains Ethanol (mg/g-substrate) S.D.
Uvaferm-43 13.84 ±0.142
Lalvin EC-1118 28.42 ±0.122
MZ-4 16.20 ±0.983
Pitchia stipilis 23.59 ±0.980
S.D= Standard deviation
E.3.5: Bioethanol Production from IL pretreated bagasse at 110°C by various yeast
strains
Strains Ethanol (mg/g-substrate) S.D.
Uvaferm-43 77.00 ±0.269
Lalvin EC-1118 59.96 ±0.707
MZ-4 78.78 ±0.943
Pitchia stipilis 62.11 ±0.191
S.D= Standard deviation
PhD Thesis
177
Appendix F
STATISTICAL ANALYSIS FOR BIOETHANOL PRODUCTION FROM
SUGARCANE MOLASSES
F.1: Analysis of variance for the effect of pH on enhanced production of bioethanol
by using Lalvin EC-1118 and MZ-4
Yeast
Strains
Sum of
Squares
df Mean
Square
F Sig.
Lalvin
EC-1118
Between
Groups
26.426 6 4.404 215.093 .000
Within
Groups
.287 14 .020
Total 26.712 20
MZ-4 Between
Groups
22.319 6 3.720 166.206 .000
Within
Groups
.313 14 .022
Total 22.632 20
F.2: Analysis of variance for the effect of temperature on enhanced production of
bioethanol by using Lalvin EC-1118 and MZ-4
Yeast
strains
Sum of
Squares
df Mean
Square
F Sig.
LalvinE
C1118
Between
Groups
13.409 4 3.352 83.808 .00
Within Groups .400 10 .040
Total 13.809 14
MZ4 Between
Groups
15.127 4 3.782 77.705 .00
Within Groups .487 10 .049
Total 15.613 14
df= degree of freedom
PhD Thesis
178
F.3: Analysis of variance for the effect of inoculum size on enhanced production of
bioethanol by using Lalvin EC-1118 and MZ-4
Yeast
Strains
Sum of
Squares
df Mean
Square
F Sig.
LalvinEC
-1118
Between
Groups
.420 4 .105 4.145 .031
Within
Groups
.253 10 .025
Total .673 14
MZ4 Between
Groups
.444 4 .111 3.964 .035
Within
Groups
.280 10 .028
Total .724 14
df= degree of freedom; Sig.= P value
F.4: Analysis of variance for the effect of inoculum age on enhanced production of
bioethanol by using Lalvin MZ-4
Yeast
Strains
Sum of
Squares df
Mean
Square F Sig.
LalvinE
C1118
Between
Groups 4.363 3 1.454 56.290 .000
Within
Groups .207 8 .026
Total 4.569 11
MZ4 Between
Groups 8.516 3 2.839 89.640 .000
Within
Groups .253 8 .032
Total 8.769 11
df= degree of freedom
PhD Thesis
179
F.5: Analysis of variance for the effect of inoculum size on enhanced production of
bioethanol by using Lalvin EC-1118
df= degree of freedom
Nitrogen
Source
Sum of
Squares
df Mean
Square
F Sig.
Urea Between
Groups
1.802 2 .901 28.964 .001
Within
Groups
.187 6 .031
Total 1.989 8
Ammonium
Chloride
Between
Groups
1.236 2 .618 12.930 .007
Within
Groups
.287 6 .048
Total 1.522 8
Ammonium
Nitrate
Between
Groups
.420 2 .210 10.500 .011
Within
Groups
.120 6 .020
Total .540 8
Ammonium
Sulfate
Between
Groups
.060 2 .030 1.000 .422
Within
Groups
.180 6 .030
Total .240 8
Diammonium
phosphate
Between
Groups
.696 2 .348 9.206 .015
Within
Groups
.227 6 .038
Total .922 8
PhD Thesis
180
F.6: Analysis of variance for the effect of inoculum size on enhanced production of
bioethanol by using MZ-4
df= degree of freedom
df= degree of freedom
Nitrogen
Source
Sum of
Squares
df Mean
Square
F Sig.
Urea Between
Groups .949 2 .474 19.409 .002
Within
Groups .147 6 .024
Total 1.096 8
Ammonium
Chloride
Between
Groups .140 2 .070 1.909 .228
Within
Groups .220 6 .037
Total .360 8
Ammonium
Nitrate
Between
Groups 2.722 2 1.361 53.261 .000
Within
Groups .153 6 .026
Total 2.876 8
Ammonium
Sulfate
Between
Groups .140 2 .070 3.500 .098
Within
Groups .120 6 .020
Total .260 8
Diammonium
Phosphate
Between
Groups .380 2 .190 19.000 .003
Within
Groups .060 6 .010
Total .440 8
PhD Thesis
181
F.7: Analysis of variance for the effect of chelating agents on enhanced production
of bioethanol by using Lalvin EC-1118
Chelating
agents
Sum of
Squares
df Mean
Square
F Sig
.
EDTA Between
Groups
5.056 7 .722 23.427 .000
Within
Groups
.493 16 .031
Total 5.550 23
Potassium
Ferrocyanide
Between
Groups
6.240 7 .891 38.204 .000
Within
Groups
.373 16 .023
Total 6.613 23
Sodium
potassium
tartarate
Between
Groups
2.660 7 .380 17.208 .000
Within
Groups
.353 16 .022
Total 3.013 23
df= degree of freedom
PhD Thesis
182
F.8: Analysis of variance for the effect of chelating agents on enhanced production
of bioethanol by using MZ-4
Chelating
agents
Sum of
Squares
df Mean
Square
F Sig
.
EDTA Between
Groups
12.905 7 1.844 94.140 .000
Within
Groups
.313 16 .020
Total 13.218 23
Potassium
Ferrocyanide
Between
Groups
27.827 7 3.975 238.514 .000
Within
Groups
.267 16 .017
Total 28.093 23
Sodium
potassium
tartarate
Between
Groups
30.467 7 4.352 307.227 .000
Within
Groups
Total .227 16 .014
df= degree of freedom
PhD Thesis
183
F.9: Analysis of variance for the effect of fed batch fermentation on enhanced
production of bioethanol by using Lalvin EC-1118
Sum of
Squares
df Mean
Square
F Sig.
Between
Groups
28.772 6 4.795 3.622 .013
Within
Groups
27.805 21 1.324
Total 56.577 27
df= degree of freedom
F10: Analysis of variance for the effect of fed batch fermentation on enhanced
production of bioethanol by using MZ-4
Sum of
Squares
df Mean
Square
F Sig.
Between
Groups
21.528 6 3.588 3.065 .026
Within
Groups
24.585 21 1.171
Total 46.113 27
df= degree of freedom
PhD Thesis
184
Appendix G
Statistical Analysis for Bioethanol Production from Bagasse
G.1.1: Analysis of variance for the glucose concentration released from untreated
and autohydrolyzed samples during enzymatic hydrolysis
Sum of
Squares
df Mean
Square
F Sig.
Between
Groups
20.170 4 5.043 833.1
70
.000
Within
Groups
.030 5 .006
Total 20.201 9
df= degree of freedom
PhD Thesis
185
G.1.2: Post hoc Tukey HSD multiple comparisons for the glucose concentration released from untreated and pretreated
bagasse samples during enzymatic hydrolysis
(I)
Pretreatme
nt
(J)
Pretreatment
Mean Difference (I-
J)
Sig. 95% Confidence Interval
Lower
Bound
Upper Bound
Untreated
Control
Autohydrolysis-190C -1.90938* .000 -2.2215 -1.5973
Autohydrolysis-205 C -3.06535* .000 -3.3774 -2.7533
Water treated- 110C -.35547* .030 -.6675 -.0434
IL- 110 C -3.57406* .000 -3.8861 -3.2620
Autohydro
lysis-190C
Untreated Control 1.90938* .000 1.5973 2.2215
Autohydrolysis-205 C -1.15597* .000 -1.4680 -.8439
Water treated- 110C 1.55392* .000 1.2418 1.8660
IL- 110 C -1.66467* .000 -1.9768 -1.3526
Autohydro
lysis-205 C
Untreated Control 3.06535* .000 2.7533 3.3774
Autohydrolysis-190C 1.15597* .000 .8439 1.4680
Water treated- 110C 2.70988* .000 2.3978 3.0220
IL- 110 C -.50871* .007 -.8208 -.1966
Water
treated-
110C
Untreated Control .35547* .030 .0434 .6675
Autohydrolysis-190C -1.55392* .000 -1.8660 -1.2418
Autohydrolysis-205 C -2.70988* .000 -3.0220 -2.3978
IL- 110 C -3.21859* .000 -3.5307 -2.9065
IL- 110 C Untreated Control 3.57406* .000 3.2620 3.8861
Autohydrolysis-190C 1.66467* .000 1.3526 1.9768
Autohydrolysis-205 C .50871* .007 .1966 .8208
Water treated- 110C 3.21859* .000 2.9065 3.5307
*. The mean difference is significant at the 0.05 level.
PhD Thesis
186
G.2.1: Analysis of variance for the xylose concentration released from untreated and
pretreated bagasse samples during enzymatic hydrolysis
Sum of
Squares
df Mean
Square
F Sig.
Between
Groups
2.388 4 .597 1990.823 .000
Within
Groups
.001 5 .000
Total 2.389 9
df= degree of freedom
PhD Thesis
187
G2.2: Post hoc-Tukey HSD multiple comparisons for the xylose concentration released from untreated and pretreated
bagasse samples during enzymatic hydrolysis
(I)
Pretreatment
(J) Pretreatment Mean
Difference
(I-J)
Std. Error 95% Confidence Interval
Lower
Bound
Upper
Bound
Untreated
Control
Autohydrolysis-190C -.40369* .01732 -.4732 -.3342
Autohydrolysis-205 C -.21721* .01732 -.2867 -.1477
Water treated- 110C -.14763* .01732 -.2171 -.0782
IL- 110 C -1.36986* .01732 -1.4393 -1.3004
Autohydrolysi
s-190C
Untreated Control .40369* .01732 .3342 .4732
Autohydrolysis-205 C .18648* .01732 .1170 .2559
Water treated- 110C .25606* .01732 .1866 .3255
IL- 110 C -.96618* .01732 -1.0356 -.8967
Autohydrolysi
s-205 C
Untreated Control .21721* .01732 .1477 .2867
Autohydrolysis-190C -.18648* .01732 -.2559 -.1170
Water treated- 110C .06958* .01732 .0001 .1390
IL- 110 C -1.15265* .01732 -1.2221 -1.0832
Water
treated- 110C
Untreated Control .14763* .01732 .0782 .2171
Autohydrolysis-190C -.25606* .01732 -.3255 -.1866
Autohydrolysis-205 C -.06958* .01732 -.1390 -.0001
IL- 110 C -1.22224* .01732 -1.2917 -1.1528
IL- 110 C Untreated Control 1.36986* .01732 1.3004 1.4393
Autohydrolysis-190C .96618* .01732 .8967 1.0356
Autohydrolysis-205 C 1.15265* .01732 1.0832 1.2221
Water treated- 110C 1.22224* .01732 1.1528 1.2917
*. The mean difference is significant at the 0.05 level.
PhD Thesis
188
G.3.1. Analysis of variance for the production of bioethanol from pretreated
bagasse by using various yeast strains
Sum of
Squares df
Mean
Square F Sig.
Between
Groups 24820.451 4 6205.113 178.043 .000
Within Groups 1219.809 35 34.852
Total 26040.260 39
df= degree of freedom
PhD Thesis
189
G.3.2. Post hoc tukey HSD multiple comparisons for the production of bioethanol from pretreated bagasse by using various
yeast strains
(I) Pretreatment (J) Pretreatment
Mean
Difference
(I-J) S.D Sig.
95% Confidence Interval
Lower
Bound Upper Bound
Untreated
control
Water treated 110C -9.41500* 2.95177 .023 -17.9015 -.9285
IL-110C -58.35875* 2.95177 .000 -66.8453 -49.8722
Autohydrolysis-190 C -46.21875* 2.95177 .000 -54.7053 -37.7322
Autohydrolysis 205C -58.51000* 2.95177 .000 -66.9965 -50.0235
Water
treated 110C
Untreated control 9.41500* 2.95177 .023 .9285 17.9015
IL-110C -48.94375* 2.95177 .000 -57.4303 -40.4572
Autohydrolysis-190 C -36.80375* 2.95177 .000 -45.2903 -28.3172
Autohydrolysis 205C -49.09500* 2.95177 .000 -57.5815 -40.6085
IL-110C Untreated control 58.35875* 2.95177 .000 49.8722 66.8453
Water treated 110C 48.94375* 2.95177 .000 40.4572 57.4303
Autohydrolysis-190 C 12.14000* 2.95177 .002 3.6535 20.6265
Autohydrolysis 205C -.15125 2.95177 1.000 -8.6378 8.3353
Autohydroly
sis-190 C
Untreated control 46.21875* 2.95177 .000 37.7322 54.7053
Water treated 110C 36.80375* 2.95177 .000 28.3172 45.2903
IL-110C -12.14000* 2.95177 .002 -20.6265 -3.6535
Autohydrolysis 205C -12.29125* 2.95177 .002 -20.7778 -3.8047
Autohydroly
sis 205C
Untreated control 58.51000* 2.95177 .000 50.0235 66.9965
Water treated 110C 49.09500* 2.95177 .000 40.6085 57.5815
IL-110C .15125 2.95177 1.000 -8.3353 8.6378
Autohydrolysis-190 C 12.29125* 2.95177 .002 3.8047 20.7778
*. The mean difference is significant at the 0.05 level.
PhD Thesis
189