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XYLITOL FROM OIL PALM EMPTY FRUIT BUNCH BY CANDIDA GUILLIERMONDII: FERMENTATION AND KINETIC STUDY MANZAILATUL AIRENNE SULAIMAN UNIVERSITI SAINS MALAYSIA 2009

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Page 1: XYLITOL FROM OIL PALM EMPTY FRUIT BUNCH BY …eprints.usm.my/...oil_palm_empty...fermentation_and_kinetic_study.pdf · xylitol from oil palm empty fruit bunch by candida guilliermondii:

XYLITOL FROM OIL PALM EMPTY FRUIT BUNCH BY CANDIDA GUILLIERMONDII: FERMENTATION AND KINETIC STUDY

MANZAILATUL AIRENNE SULAIMAN

UNIVERSITI SAINS MALAYSIA

2009

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XYLITOL FROM OIL PALM EMPTY FRUIT BUNCH BY CANDIDA GUILLIERMONDII: FERMENTATION AND KINETIC STUDY

By

MANZAILATUL AIRENNE SULAIMAN

Thesis submitted in fulfillment of the requirements for the degree

of Master of Science

APRIL 2009

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ACKNOWLEDGEMENTS

In the name of Allah, the Most Gracious and the Most Merciful

All praises to Allah for the strengths and His blessing in completing this

study. Special appreciation goes to my supervisor, Associate Professor Dr. Mashitah

Bt Mat Don for her excellent, patient guidance and infinite suggestions and help

throughout this research work. Not forgotten to my former supervisor Dr. Jyoti

Prasad Choudhury for his support, knowledge and help in completing this research

work.

I would like to express my appreciation to the Dean School of Chemical

Engineering, Prof. Abdul Latif Ahmad which was my co-supervisor for the help and

support towards my postgraduate affairs. My acknowledgement also goes to

administrative staff and technician in the school for their valuable help.

Sincere thanks to all my friends especially Huda, Midah, Yus Azila, Dila,

Lin, Siti, Zali, Aziah, Tijah, K.Min, K.Ina and others for their kindness and moral

support during my study. Thank you for the friendship and memories.

Last but not least, my depeast gratitude goes to my beloved parents; Mr

Sulaiman B. Kolib and Mrs. Zaleha Samsudin and also to my brothers and sister for

their endless love, prayers and encouragement. To those who indirectly contributed

in this research, your kindness means a lot to me. Thank you very much.

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TABLE OF CONTENT

Page ACKNOWLEDGEMENTS ii

TABLE OF CONTENTS iii

LIST OF TABLES viii

LIST OF FIGURES x

LIST OF PLATES xiii

LIST OF SYMBOLS xiv

LIST OF ABBREVIATIONS xv

ABSTRAK xvii

ABSTRACT xix

CHAPTER ONE: INTRODUCTION

1.1 OIL PALM INDUSTRIES IN MALAYSIA 1

1.2 SUGAR INDUSTRIES 4

1.3 PROBLEM STATEMENT 6

1.4 RESEARCH OBJECTIVE 7

1.5 ORGANIZATION OF THE THESIS 8

CHAPTER TWO: LITERATURE REVIEW

2.1 OIL PALM RESIDUES 10

2.1.1 Processing and residues characteristic 10

2.1.2 Oil palm residues in environmental matrices: general consideration 11

2.1.3 Oil palm residues and potential utilization 13

2.2 LIGNOCELLULOSIC MATERIALS 16

2.2.1 Cellulose 17

2.2.2 Hemicellulose 17

2.2.3 Lignin 19

2.3 HYDROLYSIS OF LIGNOCELLULOSIC MATERIALS 20

2.3.1 Inhibitors 22

2.3.2 Neutralization and detoxification 26

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2.4 XYLITOL 28

2.4.1 History of xylitol production 28

2.4.2 Chemical structure of xylitol 29

2.4.3 Application and properties of xylitol 30

2.4.4 Xylitol production process 33

2.4.4(a) Batch culture 33

2.4.4(b) Continuous culture 33

2.4.4(c) Fed-batch culture 34

2.4.5 Microorganism involved in xylitol production 35

2.4.6 Parameters affecting xylitol production 39

2.4.6(a) Initial substrate concentration 39

2.4.6(b) Initial cell concentration 40

2.4.6(c) Inoculum age 40

2.4.6(d) Initial temperature 41

2.4.6(e) Initial pH 42

2.4.6(f) Different medium composition 43

2.4.6(g) Glucose and arabinose as a co substrate 44

2.4.6(h) Agitation rate 45

2.4.6(i) Limited oxygen supply 46

2.4.7 Xylitol recovery 47

2.5 FERMENTATION KINETICS AND MODELLING 50

2.5.1 Batch culture 50

2.5.1(a) Kinetics of cell growth 50

2.5.1(b) Kinetics of product formation 51

2.5.1(c) Kinetics of substrate consumption 52

2.5.1(d) Inhibition Model 53

2.6 DESIGN OF EXPERIMENT 55

2.6.1 Response surface methodology 55

2.6.2 Central composite design 56

2.6.3 Data analysis 57

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CHAPTER THREE: MATERIALS AND METHODS

3.1 CHEMICALS 59

3.2 PREPARATION OF OIL PALM EMPTY FRUIT BUNCH FIBERS 59

3.3 PROXIMATE ANALYSIS OF OIL PALM EMPTY FRUIT BUNCH

FIBERS 60

3.3.1 Proximate analysis of OPEFB hydrolysate 60

3.4 HYDROLYSIS PROCESS 61

3.4.1 Experimental set-up 61

3.4.2 Acid hydrolysis of oil palm empty fruit bunch fibers 62

3.5 NEUTRALIZATION AND DETOXIFICATION 63

3.6 FERMENTATION STUDIES 63

3.6.1 Microorganism 63

3.6.2 Preparation of growth agar media 64

3.6.3 Preparation of cell suspension/inoculum 64

3.6.4 Fermentation studies 64

3.6.4(a) Fermentation using synthetic media 65

3.6.4(b) Effect of xylose concentration 66

3.6.4(c) Effect of initial cell concentration 66

3.6.4(d) Effect of pH 66

3.6.4(e) Effect of agitation rate 66

3.6.4 (f) Optimzation of xylitol production using RSM 67

3.6.5 Fermentation using OPEFB hydrolyzate 67

3.6.6 Fermentation kinetics analysis 68

3.7 XYLITOL RECOVERY 70

3.7.1 Crystallization of synthetic sugars 71

3.7.2 Crystallization of fermentation media 71

3.8 ANALYTICAL METHODS 72

3.8.1 Determination of acid insoluble lignin 72

3.8.2 Determination of sugar component 73

3.8.3 Determination of sugar 74

3.8.4 Determination acetic acid, furfural and hydroxymethylfurfural 74

3.8.5 Determination of cell concentration 74

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CHAPTER FOUR: RESULTS AND DISCUSSIONS

4.1 PROXIMATE ANALYSIS OF OPEFB FIBERS HYDROLYZATE 75

4.2 HYDROLYSIS OF OPEFB FIBERS 77

4.2.1 Effect of temperature 77

4.2.2 Effect of initial acid concentration 80

4.3 NEUTRALIZATION AND DETOXIFICATION 86

4.4 FERMENTATION STUDIES 89

4.4.1 Fermentation of C. guilliermondii in synthetic media 89

4.4.1(a) Effect of different production media 89

4.4.1(b) Effect of initial xylose concentration 92

4.4.1(c) Effect of agitation 94

4.4.1(d) Effect of pH 96

4.4.2 Fermentation using OPEFB hydrolyzate 98

4.4.2(a) Fermentation of detoxified media 98

4.4.2(b) Fermentation in non-detoxified media 101

4.4.3 Kinetics modeling of xylitol produced by C. guilliermondii 103

4.4.3(a) Kinetics modeling of C. guilliermandii growth 104

4.4.3(b) Kinetics modeling for substrate consumption of C.

guilliermondii 106

4.4.3(c) Kinetics modeling of xylitol production 107

4.4.3(d) Inhibition study 109

4.4.4 Optimization of xylitol production by C. guilliermondii

In OPEFB hydrolyzate using Response Surface Methodology 111

4.4.4(a) Statistical analysis and development of empirical model 112

4.4.4(b) Effect of variables studied on xylitol production 116

4.5 RECOVERY OF XYLITOL 118

4.5.1 Crystallization of synthetic xylitol 118

4.5.1(a) Effect of temperature 118

4.5.1(b) Effect of xylitol concentration 119

4.5.2 Crystallization of xylitol from fermented media 120

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CHAPTER FIVE: CONCLUSIONS AND RECOMMENDATIONS

5.1 CONCLUSIONS 123

5.2 RECOMMENDATIONS 125

REFERENCES 127

APPENDIX

LIST OF PUBLICATION

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LIST OF TABLES

Page Table 2.1 Pretreatment procedures for hemocellulosic and lignocellulosic

hydrolyzates(du Preeze,1994) 27 Table 2.2 Natural occurrence of xylitol in fruits, vegetable and related

products (Jaffe, 1978) 30

Table 2.3 The relative aweetness and measured caloric content of the most widely-used sugar alcohol (Zamora, 2005) 31

Table 2.4 Filamentous fungi for xylitol production. Modified from

Sampaio et al.,(2003) 36

Table 2.5 Different types of yeast used for producing xylitol from xylose 37

Table 2.6 The influence of stirring rate on the yeast metabolism (Mussatto and Roberto,2003) 46

Table 2.7 Physical properties of xylitol (Jaffe, 1978) 49

Table 3.1 List of chemicals used in this study 59

Table 3.2 Media composition 65

Table 4.1 Proximate analysis of oil palm empty fruit bunch (OPEFB) fiber 76

Table 4.2 Component of nutrient detoxified and non-detoxified hydrolyzate 98 Table 4.3 Fermentation parameter at different xylose concentration on non-

detoxified and detoxified media 103

Table 4.4 Parameters of kinetic growth models for synthetic xylose and OPEFB hydrolyzate in a batch culture of C. guilliermondii using the logistic model 106 Table 4.5 Parameters of substrate consumption for synthetic xylose and detoxified OPEFB hydrolyzate in a batch culture of C. guilliermondii using the logistic model 107 Table 4.6 Parameters of kinetic xylitol production for synthetic xylose and detoxified OPEFB hydrolyzate in a batch culture of C. guilliermondii using the Leudeking-Piret model 108 Table 4.7 Kinetic parameters using different types of models 111 Table 4.8 Coded and actual value of variables of different levels of the CCD112

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Table 4.9 Experimental design matrix and result of the CCD 113 Table 4.10 Analysis of Variance ANOVA for quadratic model and response surface 114 Table 4.11 Concentration of fermented media after concentrated 121 Table 4.12 Crystallization performance at difference xylitol concentration 122

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LIST OF FIGURES

Page Figure 1.1 Palm oil milling process (MPOC, 2008) 3 Figure 2.1 Palm oil residues generated from oil palm plantation

(Sumathi et al., 2008) 10 Figure 2.2 Structure of cellulose (Xiang et al., 2004) 17 Figure 2.3 Structure of Xylan Hemicellulose (Sigma Aldrich, 2008) 19 Figure 2.4 Structure of lignin monomer (Deacon, 1997) 20 Figure 2.5 Structure of 5-hydroxymethylfurfural and furfural

(Marton et al., 2006) 25

Figure 2.6 Structure of xylitol (Jeffries and Jin, 2004) 30 Figure 2.7 Sequential enzymatic reaction of xylitol formation

(Eliasson et al., 2001) 38

Figure 2.8 Three types of central composite designs (Montgomery, 2001) 57 Figure 4.1 Effect of temperature on the production of xylose and glucose

during OPEFB fibre hydrolysis 78

Figure 4.2 Effect of temperature on the production of acetic acid and furfural during OPEFB fibre hydrolysis 79

Figure 4.3 Effect of acid concentration on the production of xylose and glucose, during OPEFB fibre hydrolysis (Condition: 100 oC,) 81 Figure 4.4 Effect of acid concentration on the production of acetic acid and furfural during OPEFB fibre hydrolysis (Condition: 100 oC) 82 Figure 4.5 Effect of acid concentration on the production of xylose and glucose during OPEFB fibre hydrolysis (Condition: 120 oC) 83 Figure 4.6 Effect of acid concentration on the production of xylose,

glucose, acetic acid and furfural during OPEFB fibre hydrolysis (Condition: 120 oC) 84

Figure 4.7 Effect of acid concentration on the production of xylose and glucose during OPEFB fibre hydrolysis (Condition: 130 oC) 85 Figure 4.8 Effect of acid concentration on the production of acetic acid and furfural during OPEFB fibre hydrolysis (Condition: 130 oC) 86

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Figure 4.9 Effect of neutralization and detoxification agent on the

production of xylose, glucose, acetic acid and furfural at various reaction time 88

Figure 4.10 Fermentation profiles of cell dry weight, xylose and xylitol production by C. guilliermondii in different production

media (Condition So =200g/L, 150 rpm) 91 Figure 4.11 Fermentation profiles of cell dry weight, xylose and xylitol production by C. guilliermondii at different initial xylose concentration (So) (Condition:150 rpm) 93 Figure 4.12 Fermentation profiles of cell dry weight, xylose and xylitol

production by C. guilliermondii in difference agitation rate (Condition So =250 g/L, 150 rpm) 95

Figure 4.13 Fermentation profiles of cell dry weight, xylose and xylitol production by C. guilliermondii at difference pH (Condition:150 rpm) 97 Figure 4.14 Fermentation profiles of xylitol, xylose and cell dry weight in

detoxified hydrolyzate at different concentration of xylose added 99

Figure 4.15 Fermentation profiles of xylitol, xylose and biomass in non-detoxified hydrolyzate at different concentration of xylose added 102 Figure 4.16 Comparison between Monod model with the experimental data 104 Figure 4.17 Predicted (Logistic model) and actual values of cell dry weight concentrations on synthetic and detoxified OPEFB hydrolyzate 105 Figure 4.18 Predicted (logistic model) and actual values of substrate

consumption on synthetic and detoxified OPEFB hydrolyzate 106

Figure 4.19 Predicted (Leudeking-Piret model) and actual values of xylitol production on synthetic and detoxified OPEFB hydrolyzate 108 Figure 4.20 Comparison of model prediction with the experimental data for substrate inhibition (a-Aiba Model, b- Andrew Model, c- Competitive Model) 110 Figure 4.21 Predicted and Experimental result of DoE 115 Figure 4.22 Effect of agitation rates and pH on contour plot and 3D Dimension 117 Figure 4.23 Effect of temperature on crystal development 119

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Figure 4.24 Effect of different xylitol concentration on xylitol yield 120

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LIST OF PLATES

Page Plate 3.1 Hydrolysis reactor 61

Plate 3.2 Sample for hydrolysis process 62

Plate 3.3 Crystallization unit 71

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LIST OF SYMBOLS

A, B or C Coded factor

Α Alpha (axial distance from centre point which makes the design rotatable)

βo Constant coefficient βi Coefficient for linear effect βii Coefficient for quadratic effect βij Coefficient for cross-product effect Qp Xylitol productivities g/L/h

Qs Substrate consumption g//L/h

R2 Coefficient of determination

So Initial concentration substrate g/L

Sf Final concentration substrate g/L

to Initial fermentation time hr

tf Final fermentation time hr

Xo Initial biomass concentration g/L

Xf Final biomass concentration g/L

Y Response calculated by model (dependent variables)

Yp/s Yield of product over the substrate consumption g/g

Yp/x Yield of product over the biomass g/g

Yx/s Yield of biomass over the substrate consumption g/g

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LIST OF ABBREVIATIONS

ANOVA Analysis of variance

CaO Calcium oxide

Ca(OH)2 Calcium hydroxide

CCD central composite design

CH3COOH Acetic acid

CO Carbon monoxide

CPO Crude palm oil

DoE Design of Experiment

EFB Empty fruit bunch

FFB Fresh fruit bunch

FV Final volume

g gram

GC Gas chromatography

hr hour

HPLC High performance liquid chromatography

IV Initial volume

KOH Kalium hydroxide

L liter

NAD/NADH Nicotinamide Adenine Dinucleotide

NaOH Sodium hydroxide

NOx Nitrogen oxide

OH- Hydroxide ions

OPA Oil palm ash

OPEFB Oil palm empty fruit bunch

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RI Refractive index

rpm rotation per minute

RSM Response surface methodology

SD Standard deviation

PM Particulate matters

POME Palm oil mill effluent

WHO World health organization

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XILITOL DARIPADA TANDAN KOSONG BUAH KELAPA SAWIT MENGGUNAKAN CANDIDA GUILLIERMONDII:

FERMENTASI DAN KAJIAN KINETIK

ABSTRAK

Tandan buah kelapa sawit kosong adalah salah satu bahan buangan utama

yang dihasilkan oleh kilang kelapa sawit. Bahan buangan yang mudah didapati,

murah dan boleh diguna semula ini telah dipilih sebagai bahan asas untuk

penghasilan xilitol, kerana ia mengandungi hemiselulosa, terutamanya xilan yang

boleh dihidrolisis kepada xilosa. Oleh kerana kandungan xilitol dalam sumber

semulajadi adalah sangat rendah, bahan yang mempunyai kadar harga yang rendah

dengan kandungan xilosa yang tinggi telah dikenal pasti sebagai bahan pemula.

Analisis ke atas tandan buah kelapa sawit kosong menunjukkan terdapatnya 5

sebatian utama iaitu xilosa, glukosa, lignin, asid asitik dan furfural. Kepekatan

sebatian tertinggi dikesan untuk xilosa pada 36.54 g/L. Ini menunjukkan tandan

kosong buah kelapa sawit adalah bahan yang sesuai untuk penghasilan xilitol.

Dalam proses hidrolisis, penghasilan xilosa yang paling tinggi iaitu 28.97 g/L

telah dikesan pada 120 oC, 15 minit masa tindakbalas dengan menggunakan 6% asid

sulfurik. Proses hidrolisis telah dipanjangkan ke 300 minit untuk menentukan

kehadiran bahan perencat seperti asid asitik dan furfural serta komponen gula yang

lain iaitu glukosa. Di dalam proses peneutralan dan penyahtoksikan, kombinasi

penggunaan kalsium oksida dan karbon teraktif menunjukkan kesan penurunan

perencat yang tinggi, iaitu sehingga 69% kepekatan pada asid asetik dan 61 %

kepekatan pada furfural.

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Untuk proses fermentasi, Candida guilliermondii FTI 20037 telah dipilih

sebagai biokatalis bagi penukaran xilosa kepada xilitol. Dengan menggunakan

media sintetik, penghasilan xilitol tertinggi diperolehi di dalam Media 1, pada pH

3.5, 250 ppm, kepekatan substrat permulaan 250 g/L dan saiz inokulum 10 g/L.

Penghasilan xilitol dengan menggunakan media ditoksifikasi dan media tidak-

ditoksifikasi menunjukkan penghasilan xilitol per kepekatan xilosa (Yp/s) ialah

0.73g/g dan 0.6 g/g, masing-masing. Ini menunjukkan media yang telah ditoksifikasi

adalah substrat lebih baik berbanding media tidak-didetoksifikasi.

Penggunaan model tidak berstruktur bagi pertumbuhan, penghasilan xilitol

dan penggunaan substrat telah dibandingkan. Didapati model Logistik bersesuaian

dengan pertumbuhan C. guilliermondii dan penggunaan substrat, sementara model

Leudeking-Piret pula adalah untuk penghasilan xilitol. Bagi perencatan substrat,

model Andrew telah bersesuaian dengan pemerhatian eksperimen dengan R2 =0.94.

Proses pengoptimum telah dijalankan untuk mengenalpasti penghasilan xilitol yang

tertinggi dengan menggunakan kaedah permukaan sambutan (RSM). Keadaan

optimum bagi penghasilan xilitol telah dilihat pada pH 3.5, 250 rpm (kadar

goncangan) dan saiz inokulum 10 g/L.

Xilitol telah dihablurkan pada -10 oC menggunakan kepekatan media sintetik

dan media fermentasi yang berbeza. Proses penghabluran bagi kedua-dua media

mengambil masa 4 jam dan 10 jam, masing-masing. Ini mungkin disebabkan

kehadiran bahan asing di dalam media. Pada kepekatan xilitol yang tertinggi 597

g/L, 0.49 g/g, hablur xilitol telah diperolehi dengan 91.05% penulenan.

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XYLITOL FROM OIL PALM EMPTY FRUIT BUNCH BY CANDIDA GUILLIERMONDII: FERMENTATION AND KINETIC STUDY

ABSTRACT

Oil palm empty fruit bunch (OPEFB) is one of the main wastes generated by

palm oil mills. This waste is widespread, cheap and renewable and be selected as raw

materials for xylitol production as it contains hemicellulose, comprising xylan that

can be hydrolysed to xylose. As the xylitol content is very low in other natural

sources, a low cost material with high content of xylose is identified as the starting

material.

Analysis of oil palm empty fruit bunch fibers showed that there were 5 main

compounds namely xylose, glucose, lignin, acetic acid and furfural. The highest

compound concentration was detected for xylose at 36.54 g/L. This showed that an

oil palm empty fruit bunch was a suitable material for the production of xylitol.

In hydrolysis process, the highest xylose production was detected at 120 oC,

15 min reaction time with 6% sulphuric acid at 28.97 g/L. The hydrolysis process

was prolonged up to 300 min in order to determine the production of inhibitor

components such as acetic acid and furfural, and also the presence of other sugar

component such as glucose. In neutralization and detoxification process, the

combination of calcium oxide and activated charcoal treatment showed the highest

reduction of inhibitors, which was up to 69% on acetic acid and 61% on furfural

concentration.

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For fermentation process, Candida guilliermondii FTI 20037 was chosen as a

biocatalyst for the conversion of xylose to xylitol. In synthetic media, the highest

xylitol production was obtained in Media 1 at pH 3.5, 250 rpm, initial substrate

concentration 250 g/L and inoculum size at 10 g/L. Production of xylitol using

detoxified and non-detoxified media showed that the yield of xylitol per xylose

concentration (Yp/s) were 0.73g/g and 0.6 g/g, respectively. This showed that

detoxified media was much better substrate compared to non-detoxified media.

An unstructured model taking into account growth, xylitol production and

substrate consumption were compared. It was found that Logistic model fitted well

with C. guilliermondii growth and substrate consumption, while Leudeking-piret

model was for xylitol production. For substrate inhibition, Andrew model fitted well

with the experimental observation with R2 =0.94. The optimization process was

performed to find out the optimum condition that lead to the highest production of

xylitol using Random Surface Methodology (RSM). The optimum condition for

xylitol production was observed at pH 3.5, 250 rpm agitation rate and 10 g/L of

inoculum size.

Xylitol was crystallized at -10 oC using different concentration of synthetic

and fermented media. The crystallization for both media took 4 hr and 10 hr,

respectively. This could be due to the presence of other impurities in the media. At

the highest xylitol concentration at 597 g/L, 0.49g/g xylitol crystal yield was

obtained with 91.05% of crystal purity.

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CHAPTER 1

INTRODUCTION

1.1 OIL PALM INDUSTRIES IN MALAYSIA

The Malaysian oil palm industries started in 1917 and grew slowly until

1950, when the agricultural diversification policy switches over from rubber to palm

oil. Malaysia became the largest producer and exporter of palm oil, which then

became a major agricultural industry in the country. In 2006, Malaysia produced

about 51% of the world's palm oil and 62% of world export, which will expand more

a head (Ahmad et al., 2006).

Palm oil or Elaeis guineensis act as number one fruit crops in terms of

production with 36.9 million tones for the year 2007 or 35.9% of the total edible oil

in the world (MPOC, 2007). Malaysia’s palm oil production will hit 20 million tones

by 2020 (FORBES 2007). The oil prices have reached a new price of around RM

1800 to 1900/tonne (The Star, 2009). It was able to supply 12% of the global

vegetable oil and 26% of the export trade in oils and fats (MPOC, 2006).

The total area under oil palm cultivation is over 2.65 million hectares,

producing over 8 million tones of oil annually (Basiron, 2006). The oil consists of

only 10% of the total biomass produced in the plantation. The remainder consists of

a huge amount of lignocellulosic materials such as oil palm fronds, trunks and empty

fruit bunches. According to Mahmudin and Puad (1999), the projection figures of

these residues are 7.0 million tonnes of oil palm trunks, 26.2 million tonnes of oil

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palm fronds and 23% of empty fruit bunch (EFB) per tonnes of fresh fruit bunch

(FFB) processed in oil palm mill.

An average oil palm mill can handle about 100 million tones of fresh fruit

bunches daily. Figure 1.1 shows the extraction process in one of the palm oil mills.

At the mills where oil extraction took place, solid and liquid wastes were generated.

The solid residues, mainly EFB were more than 20% of the fresh fruit weight (Ma et

al. 1993). For the liquid wastes, more than 500 kg (around 0.5 m3) is produced,

which is mainly in the form of palm oil mill effluent (POME), and are discharged

during the processing of 1.0 million tones of fresh fruit bunches (Ma et al. 1996).

Meaning that, 20 million tones of EFB and more than 50 m3 of POME will be

expected to be produced from a mill after processing 100 million tones of fresh fruit

bunches.

The EFB is a lignocellulosic raw material and act as renewable resources,

which is a valuable commodity in the market (MPOC 2007). Currently these fibers

are used as boiler fuel and potassium fertilizer. The transformation of these fibers to

a valuable food and pharmaceutical products is an advantage to the Malaysian

economics. One of the valuable products that can be produced from these fibers are

xylitol. Xylitol is a sugar alcohol, act as an artificial sweetener, which has dietary

and high technological properties (Pepper and Olinger, 1988).

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Figure 1.1 Palm oil milling process ( ____ )process (------) waste (MPOC, 2008)

Due to the need of industrial scale production and subsequent low down of

the xylitol prices, EFB represents as a low-cost starting material for sugar

production. In recent years, there has been an increasing trend towards more efficient

utilization of agro industrial residues to xylitol such as sugarcane baggase ( Marton

et al., 2006), rice straw (Mussatto and Roberto, 2004), corn cobs (Dominguez et al.,

Sterilizer

Fresh fruit bunch

Liquid Solid

Empty Fruit Bunch

Cyclone

Nut cracker

Decanter

Purifier

Cake

Palm press fiber

Palm oil kernel shell

Water (80-90oC)

Treatment ponds

Oil

Effluent

Kernel

Pack for kernel

Nut

Condensate Steam(140oC, 50 min)

Fruits

Thresher

Digester

Oil mash

Screw press

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1997) and sorghum straw (Herera et al., 2003) they provide a good substrate for

microbial cultivation.

1.2 SUGAR INDUSTRY

Sugar production was established in the seventh century AD. Since then, the

sugar industry has grown immensely. In 2008, Malaysia’s sugar production was only

84 thousand metric tons while the overall sugar consumption was 1,343 thousand

metric tons (FAPRI, 2008). Increasing demand of sugar leads to imported sugar to

meet the rising demand and compensate for the stagnant domestic production. For

example, imports for the first 5 years of the 1990s averaged 885 000 tonnes per year,

compared with 494 000 tonnes for the first-half of the 1980s, a 79 percent increase.

In recent years, sugar has been Malaysia's largest agricultural imports, with annual

sugar imports valued between US$200 to 300 million (FOA, 1997).

Sugar is an important source of food energy. During digestion, all food

carbohydrates (starches and sugars) broke down into single molecule sugars. These

sugars are absorbed from the intestine into the blood stream and travel to the cells,

where they are used to provide energy for cellular functions. In parts of the world

where people suffer from energy malnutrition and are undernourished, sugar is

valued as an inexpensive source of energy to support human activities.

But regularly eating large amounts of sugar will cause serious harm. Sugar

can cause hyperglycemia and weight gain, leading to diabetes and obesity in both

children and adults. It leached the body vital minerals and vitamins and raised blood

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pressure, triglycerides, and the bad cholesterol (LDL), thus increasing the risk of

heart disease. It causes tooth decay and periodontal disease, which leads to tooth loss

and systemic infections. Besides that, it also make a child's difficult to learn,

resulting in a lack of concentration. Both children and adults exhibit disruptive

behavior, learning disorders, and forgetfulness from sugar consumption. It initiates

auto-immune and immune deficiency disorders such as arthritis, allergies, and

asthma. It also upsets hormonal balance and supports the growth of cancer cells

(FAO, 1997). Therefore, the increasing amount of sugar in food, sweets and soft

drinks could raised some concern about health effect. World Health Organization

(2003) reported that the number of people suffer from diabetes, obesity, cancer and

cardiovascular diseases are increasing every year especially in the developing world.

In fact, about 1.2 million peoples in Malaysia are suffering from diabetes (The Star,

2006).

The Polyols sweetener industry is experiencing a rapid growth because of the

increasing consumer demand for sugar-free and reduced calorie products (Mussatto

et al., 2006a). The sweeteners experiencing this rapid growth are the sugar alcohols

such as xylitol, sorbitol, mannitol and maltitol. The name polyols refers to chemical

compounds containing multiple hydroxyl groups. Sugar alcohols, a class of polyols,

are commonly added to foods because of their lower caloric content than sugars;

however they are also generally less sweet, and are often combined with high

intensity sweeteners (Emodi, 1978).

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Sugar alcohols are usually incompletely absorbed into the blood stream from

the small intestines which generally results in a smaller change in blood glucose than

sucrose. This property makes them become a popular sweetener among diabetics and

people on low-carbohydrate diets. However, as for many other incompletely

digestible substances (such as dietary fiber), over consumption of sugar alcohols can

lead to bloating, diarrhea and flatulence because they are not absorbed in the small

intestine. Some individuals experience such symptoms even in a single-serving

quantity. With continuous use, most people develop a degree of tolerance to sugar

alcohols and no longer experience these symptoms (Parajo et al., 1998)

In Asia, xylitol is particularly in demand from the gum manufacturers; it was

estimated that 80 to 90 per cent of chewing gum sold in the region now has the

xylitol in their formulations. The China based company Futaste currently produces

35,000 tons of xylitol each year, as well as 20,000 tons of xylose and other types of

sweeteners from corn cobs. The xylitol are now available in the market with the

prices at RM 50 per kg (Charlotte, 2008). Hopefully with the development of

biotechnological production of xylitol, the prices could be cheaper as consumer can

use xylitol rather than other ordinary sweetener.

1.3 PROBLEM STATEMENT

Among various agriculture wastes in Malaysia, oil palm empty fruit bunch

(EFB) is regarded as a promising agricultural resource as it is rich in cellulose and

hemicellulose but is not effectively utilized. The industrial use of oil palm empty

fruit bunch contributes to a reduction of an environmental pollution caused by their

disposal and lost of potentially valuable resources. EFB on the other hand is known

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to give rise to deposits and corrosion problems. The hydrolysis of EFB to produce

xylose solution can be a good alternative for this abandone product. This process has

a double consequentces, i.e: the elimination of a waste and the production of a value-

added product.

The industrial production of xylitol is based on the catalytic hydrogenation of

xylose. This process requires the use of high pressure and temperature and extensive

xylose purification steps, thus making a final product with a relatively high

production cost. An alternative way to produce xylitol is by the biotechnological

route, which can be more economically viable because it requires only a mild

condition of temperature and pressure, and it eliminates the purification step since

the microorganism specifically acts on xylose-to-xylitol bioconversion

(Winkelhausen and Kusmanova, 1998). Microbial production of xylitol from

agriculture wastes containing hemicellulose could be the best approach because it

has a potential to realize cheaper production of xylitol with low environmental effect

by effective utilization of renewable resources such as agricultural waste, oil palm

empty fruit bunch (OPEFB) fibers.

1.4 RESEARCH OBJECTIVE

The main objective of this project is to study xylitol production by C.

guilliermondii using oil palm empty fruit bunch hydrolysate as a substrate. The

measurable objectives are:

1. to study the effect of multiple hydrolysis variable (reaction temperature,

acid concentration and time) on the formation of xylose

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2. to investigate the effect of various fermentation parameters for the

production of xylitol by C. guilliermondii using synthetic and oil palm

empty fruit bunch hydrolysate

3. to optimize fermentation variables for the production of xylitol in oil

palm hydrolysate using Design of Experiment (DoE)

4. to compare kinetic models of microbial growth, xylitol production, xylose

consumption and substrate inhibition by the tested yeast

5. To crystallize xylitol using synthetic and fermented media

1.5 ORGANIZATION OF THE THESIS

This thesis consists of five chapters that covers important details regarding

this research.

Chapter One introduces the oil palm industries and the sugar industries in

Malaysia. The problem statement is stated to give clear aims followed by the

objectives of the study.

Chapter Two describes the fundamental characteristic of biomass residues

and lignocellulosic materials. Explanations on hydrolysis process and neutralization

and detoxification process were also discussed. In addition, the importance of xylitol

production, fermentation process and xylitol recovery were also looked at. The last

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section discussed in details on the fermentation kinetics and Design of Experiments

(DOE) for optimization and process parameters.

Chapter Three refers to the material and methods describing the experimental

procedures of the present study. This chapter also covers the acid hydrolysis process,

fermentation, kinetic and optimization studies, crystallization and analytical

procedures.

Chapter Four discussed the experimental result together with the data analysis

of various operating condition and process parameters. The detail explanations of the

result are been divided into three main processes; hydrolysis, fermentation and

crystallization. The kinetics and optimization of fermentation process using

Response Surface Methodology have been discussed through this section. Each of

the result will be followed by the discussion and comparison between the present

results and the results obtained by others researchers.

Chapter five gives the overall conclusion based on the result obtained in

Chapter 4. Recommendations for future research are also given in the chapter.

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CHAPTER 2

LITERATURE REVIEW

2.1 OIL PALM RESIDUES

2.1.1 Processing and residues characteristic

Oil palm is a multipurpose plantation and also a prolific biomass producer

which can be used as raw materials for value added industries (Basiron and Simeh,

2005). Fresh fruit bunch contains only 21% palm oil, while the rest are 6-7% palm

kernel, 14-15% fiber, 6-7% shell and 23% empty fruit bunch (EFB) left as biomass

(Umikalsom et al., 1997). Oil palm residues (including shell, fibre and kernel) are

cheap and abandoned materials produced during palm oil milling process (Figure

2.1). About 80% of these solid wastes were used as boiler fuel in many industries

and 20% were left behind (Pansamut et al., 2003).

Figure 2.1 Palm oil residues generated from oil palm plantation (Sumathi et al., 2008)

Oil palm plantation

Fresh fruit bunch Oil palm trunk

Empty fruit bunch

Oil palm frond

Palm press fiber

Palm kernel cake Palm kernel shell

Mesocarp fiber

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Oil palm empty fruit bunch (OPEFB) is generated as waste material by palm

oil mills which consist of fibers. The fibrous materials were physically stick together

to form vascular bundles. EFB from the mill contains 30.5% lignocellulose, 2.5% oil

and 67% water. The main constituents of the lignocellulose were cellulose (45%),

hemicellulose (32.8%) and lignin (20.5%). Of the hemicellulose, pentosan was

27.3%. It is estimated that oil palm empty fruit bunch comprises of 24% xylan, a

sugar polymer made of pentose sugar (Muthurajah, 1981; Husin et al., 1985; Ellis

and Paszner, 1994).

Oil palm fiber is a non-hazardous biodegradable material extracted from oil

palm empty fruit bunch (EFB) through decortication process. The fibers are clean,

non-carcinogenic, free from pesticide and soft parenchyma cells. The empty fruit

bunch is normally composed of a main stalk and numerous sharp and spines

spikelets. The fresh sterilized EFB holds about 65% moisture, 30% dry matter and 2-

5% crude palm oil (Husin et al., 2002).

Oil palm fronds are available daily throughout the year when the palms were

pruned during the harvesting of fresh fruit bunch. Oil palm trunk is obtained during

the replanting of the oil palm trees. EFB, mesocarp fiber and shell were collected

during the pressing of sterilized fruits (Gurmit et al., 1999).

2.1.2 Oil palm residues in environmental matrices: general consideration

The oil palm industries produced more than one hundred million tonnes of

residues worldwide. One hectare of oil palm plantation generates about 21.62 tonnes

per year of biomass residues. Fronds and EFB were the most residues produced

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which was 50.31% and 20.44%, respectively (Singh et al., 1999; Saka, 2005; Goyal

et al., 2006).

The utilization of biomass residues from palm oil by-products (fiber & shell)

as fuel source were identified as the main cause of the emission released.

Economically, the usage of palm residues as fuel is seen as productive as this

material will not be wasted. However the combustion process in the furnace of the

boiler released the emission of particulate matters (PM), carbon monoxide (CO),

nitrogen oxide (NOx) and sulphur dioxide (SOx). Due to that, monitoring and control

of these pollutants from the palm oil mill is of great concern to the community

(Prasertsan and Prasertan, 1996).

The residues generated at the palm oil mills such as empty fruit bunches,

fibres and kernel shells can be used to produce electricity to supply the national grid.

Technologies are now available to harness the biogas from effluent ponds of the

mills for power generation. If the biogas is fully exploited, more of the fibre and

kernel shell can be alternatively used for power generation to supply the national grid

or for composite fibreboard production. In the future, the carbon credit derived from

the use of biogas and biomass for power generation may contribute further revenue

to the country. For example, methane (biogas) fetches USD 10/tonne of tradable

carbon under the Kyoto Protocol when it came into effect in the year 2008 (Basiron

and Simeh, 2005).

MPOB research has also shown that palm oil is a good source for liquid fuel.

It has been established that CPO can be burnt as fuel. During the 2001 downturn in

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palm oil prices, it was also shown that CPO can be blended with medium fuel oil to

be used as fuel for boilers. Up to 6518 tons of CPO was burnt as fuel in the national

utilities power plant at Prai, Pulau Pinang. The bigger potential is in respect of

conversion of palm oil into methyl esters (palm diesel). Road trials involving buses

have shown that it can be used as a diesel substitute with positive environmental

effects. The palm diesel plant can also produced beta carotenes and vitamin E that

can contribute to the viability of the biodiesel project. The other option that MPOB

research has unfolded is the possibility of blending processed palm oil with diesel

(5%-10%). Malaysia is currently in the process of preparing the regulatory

framework to enable the government to mandate the use of biofuel when the

situation warrants such an intervention (MPOC, 2008).

2.1.3 Oil palm residues and potential utilization

The supply of oil palm residues from the oil palm and palm oil processing by-

products is seven times the availability of natural timber. Each year, the oil palm

industries in Malaysia generate more than 30 million tonnes of residues in the forms

of empty fruit bunches, oil palm trunks and oil palm fronds. Palm residues such as

empty fruit bunches and trunks are being used for commercial products (e.g. pulp

and paper, medium density fibreboard, automotive components etc.). Effective

utilization of palm residues into value-added products has the potential to generate

another RM 20 billion in the next 10-15 years (Basiron and Simeh, 2005).

Currently, oil palm residues are converted into various types of value added

products via several conversion technologies that are readily available. For example,

fibers from EFB were found to be an ideal material for the making of mattresses,

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seats, insulation and etc (Basiron and Simeh, 2005). EFB has been investigated as a

raw material for building materials, solid fuel pellets, chemical products,

particleboard, fiberboards, blockboard, and pulp and paper (Muthurajah, 1981;

Kobayashi et al.,1985; Husin et al., 1985; Gabriele, 1995).

The latest researches by MPOB onto EFB are to convert EFB into paper-

making pulp. The pulp is then bleached using the total chlorine-free (TCF) methods

to obtain sheets of paper. Pulp and paper from oil palm biomass can be used in many

ways such as cigarette paper and bond paper for writing (Gurmit et al., 1999; MPOC

2006).

Palm fibers are versatile and stable and can be processed into various

dimensional grades to suit specific applications such as mattress cushion production,

erosion control, soil stabilization/compaction, landscaping and horticulture, ceramic

and brick manufacturing, thermoplastic filler, flat board manufacturing, paper

production, acoustics control, livestock care, compost, fertilizer and animal feed

(Sumathi et al., 2008).

Oil Palm Ash (OPA) produced from incinerating the empty fruit bunch were

used as fertilizer due to its high organic and nutrient content beneficial to crop. In the

other cases, fibers, shell and empty fruit bunches were used as a source of energy for

the processing mill itself to generate heat and electricity (Yusoff, 2006).

The research by local scientist proved that palm kernel, EFB, palm shells and

stones can be converted to oil palm activated carbon (Jia and Aik, 2002; Jia and Aik,

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2000). The oil palm activated carbon has been used to treat toxic air such as carbon

monoxide (CO) and SOx (Sumathi et al.,2008).

The oil palm trunk is converted to various types of wood such as saw-wood

and ply-wood or lumber. Oil palm lumber has been successfully utilized as core

residues in the production of blackboard. The sawn-wood produced from oil palm

can be used to make furniture but not for building structure due to its low specific

density. Oil palm trunk also has been used to produce particleboard with chemical

binders. Some of the trunks were mixed with EFB and oil palm press fiber to be

combusted and produced energy (Gurmit et al., 1999).

Oil palm fronds were also a source of food for ruminants (cattle and goats).

Fronds were left to rot in between the rows of oil palm trees in the plantation for soil

conservation, increased the fertility of the soil, increased the amount of water

retained in the soil, erosion control and provide a source of nutrient to the growing

oil palm trees (nutrients is recycled as a long term benefits) (Husin et al., 2002).

Palm oil mill effluent (POME), a high volume liquid waste which are non

toxic has been used for cellulase production. Cellulase was identified as one of the

key enzyme degrading cellulose (Kotchoni et al., 2003). It finds extensive

application in food, fermentation and textile industries (Muthuvelayudham and

Viruthagiri, 2006).

Oil palm biomass can also be potential feedstock raw materials to chemical

and biochemical industry. The cellulose component can be hydrolyzed to yield

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glucose from which ethanol, citric acid, butanol and other single cell protein can be

obtained through chemical and microbiological transformation. Hemicelluloses, also

present in the biomass can yield pentoses especially xylose which upon hydrolysis

can be converted to xylitol, furfural, furan, resins and furfuryl alcohol. The lignin

fraction of oil palm biomass is a potential source of phenolic resins (Basiron and

Simeh, 2005).

However, these renewable materials can be alternatively used for producing

valuable chemical products (fuel, and chemical feedstock) by applying the

thermochemical conversion process, including pyrolysis, liquefaction and

gasification as well as supercritical fluid extraction methods (Yaman, 2004).

2.2 LIGNOCELLULOSIC MATERIALS

Lignocellulosic material is an abundant and inexpensive source of sugar

which can be microbiologically converted to industrial products such as fuel alcohol,

chemical and protein for food and feed purpose. Lignocellulosic biomass, such as

corn stover, wheat bran, sugar cane baggase and oil palm empty fruit bunch were

easily available and produced in a large scale in the agriculture developing country.

It can be directly or indirectly used for the production of biomolecules and

commodity chemicals. However, some of these applications were limited by the

close association exist among the three main components in lignocellulosic:

cellulose, hemicellulose and lignin. Therefore clear understandings of the chemistry

towards identifying the reason why it was so resilient to biological process such as

hydrolysis and fermentation is urgently needed (Ramos, 2003).

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2.2.1 Cellulose

Cellulose is a straight chain polymer that consists of glucose unit linked

together by β (1-4) glycosidic bonds (Figure 2.2). It is an insoluble molecule

consisting of 2000 - 14000 residues. The size of cellulose molecule is given in terms

of its degree of polymerisation. However conformational analysis of cellulose

indicated that cellobiose is the basic structural unit rather than glucose (Ramos,

2003).

Cellulose is found in large amounts in nearly all plants, and is potentially a

major food source. The cellulose chain bristles with polar -OH groups. These groups

form many hydrogen bonds with OH groups on adjacent chains, bundling the chains

together. The chains also pack regularly in places to form hard, stable crystalline

regions that give the bundled chains even more stability and strength. The effect of

the bonding by hydrogen bond increased the rigidity of cellulose and causes the

cellulose highly insoluble in most solvent (Jeoh, 1998).

C

C

C

C

O

OH

OH H

H

CH2OH

O

HC

O

C

H C

C

C

OOH

OHH

H

CH2OH

HC

O

C

H

C

C

C

O

OH

OH H

H

CH2OH

OC

H

Figure 2.2 Structure of cellulose (Xiang et al., 2004)

2.2.2 Hemicellulose

Hemicellulose is the second most abundant natural polysaccharides after

cellulose. It comprises of one fourth to one third of most plant materials and this

amount will vary according to the particular plant species. Hemicelluloses are linear

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polymers composed of cyclic 5-carbon and 6-carbon sugars (polysaccharides). They

are mainly composed of pentose (xylose, rhamnose and arabinose) and hexose

(glucose, mannose and galactose) sugars which can be reduced to monomeric sugars

primarily to xylose and glucose by hydrolysis with mineral acid (Saha, 2003).

Hemicellulose is considerably easier to hydrolyze than cellulose. Studies

have shown that hydrolysis of hardwood hemicellulose at 120-140 oC using 2.5%

H2S04 gave xylose yields exceeding 80% in most cases (Kim and Lee, 1987).

Many studies utilized the hemicellulose portion of agriculture residues like

Eucalyptus grandis (Silva et al., 1998a), rice straw (Roberto et al., 1994), aspen

wood hemicellulosic hydrolyzate ( Preziosi-Belloy et al., 2000), barley bran (Cruz et

al., 2000), hybrid polar wood chips (Dominguez et al., 1997), and corn cobs (Rivas

et al., 2003) for xylitol production.

The hemicellulose content of softwoods and hardwood differ significantly

(Fengel and Wegener, 1989). Hardwood hemicellulose mainly composed of highly

acetylated heteroxylan, generally classified as para-o-methyl glucoronoxylan.

Hexosans were also present but only in small amount (Ramos, 2003). In contrast,

softwoods have two principal hemicelluloses: galacto-glucomannan (70% mannan),

which made up approximately 60% of the total hemicellulose content, and arabino-4-

0-methylglucuronoxylan (65% xylan), which constitutes the remaining 40%. The

amount of galactose/mannan and arabinan/xylan was used to estimate the quantities

of the major and minor hemicellulose component of the wall (Timell, 1967; Highley,

1987). Softwood hemicellulose contained a high proportion of mannose units and

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more galactose unit than hardwood hemicellulose whereas hardwood hemicellulose

contained a high proportion of pentose (Fengel and Wegener, 1989).

Xylan is a major constituent of hemicellulose (Figure 2.3). It is a

polysaccharide that can be hydrolyzed into D-xylose, which is also known as wood

sugar. Xylan consists of about 200 β-xylopyranose residues, linked together by 1, 4-

glycosidic bonds. However they contain smaller propartions of uronic acid, but are

more highly branched and contain large proportion of L-arabinofuranosyl unit (Saha,

2003).

C

C

C

C

O

OH

OH C

O

C

C

C

C

O

OH

OH C

O

C

C

C

C

O

OH

OH C

O

C

C

C

C

O

OH

OH C

Xylanase

Xylan Hemicellulose

O

O

Figure 2.3 Structure of Xylan Hemicellulose (Sigma Aldrich, 2008)

2.2.3 Lignin

In plant tissues, hemicelluloses are generally combined with lignin (Fengel

and Wegener, 1989). Lignin is a three dimensional polymer of aromatic compounds

covalently linked with xylan in hardwood and galactoglucomannan in softwoods

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(Garg et al., 2007). Its structure composed of phenylpropane monomer namely para-

coumaryl alcohol, coniferly alcohol and sinaply alcohol, which were generally

referred as cinnamyl alcohol, and were commonly called lignin C9-units (Figure

2.4). It contributes to approximately 15% to 35% of the dry mass of softwoods,

hardwoods and woody grasses. Lignin is deposited between individual wood fibers

and act as an intercellular adhesive, binding individual wood fibers together. Lignin

was usually insoluble in all solvents, unless it is degraded by physical or chemical

treatments (Ramos, 2003).

OH

OH

12

34

5

6

p-coumaryl alcohol

OH

OH

OCH3

Sinapyl alcohol

CH3O

OH

OH

OCH3

Coniferyl alcohol

Figure 2.4 Structures of lignin monomer (Deacon, 1997)

2.3 HYDROLYSIS OF LIGNOCELLULOSIC MATERIALS

Hydrolysis is a process of splitting compound into fragment by the addition

of water. In acid hydrolysis process, acid is used as a catalyst in the splitting process.

The hydrolysis process in dilute acid medium is very complex, as the substrate is in a

solid phase and the catalyst in a liquid phase. Dilute acids leads to a limited

hydrolysis, this occurs in the hydrolysis of hemicellulosic fraction, leaving the

cellulose and lignin fraction almost unaltered (Karimi et al., 2006)

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Dilute acid hydrolysis appeared to be in the best position from the economic

viewpoint (Wyman, 1994). Therefore using selected operational condition, it is

possible to hydrolyze almost quantitatively hemicelluloses leaving the cellulose and

lignin in the solid residue, which can be processed for the conversion of glucose

solution to ethanol through fermentation process (Parajo et al., 1995) and the

production of paper pulp (Grethlein and Converse, 1991).

Sulphuric acid (Nguyen et al, 2000), hydrochloric acid (Springer, 1966), or

acetic acid (Conner and Lorenz, 1986) are acids commonly employed as catalysts.

These acids released protons that break the heterocyclic ether bonds between the

sugar monomers in the polymeric chains formed by the hemicelluloses and cellulose.

The breaking of these bonds released several compounds, mainly sugars such as

xylose, glucose and arabinose. Other compounds released are oligomers, furfural and

acetic acid. A quantitative hydrolysis of the hemicelluloses can be performed almost

without damage to the cellulose because the bonds in hemicelluloses are weaker than

in cellulose (Bungay, 1992).

In dilute-acid hydrolysis the hemicellulose fraction is depolymerized at lower

temperatures than the cellulose fraction. If higher temperatures (or longer residence

times) were applied, the formed monosaccharide from the hemicellulose will degrade

(Saeman, 1945), which gave rise to furan compounds and carboxylic acids

(Taherzadeh et al., 1997; Larsson et al., 1999).

The degradation of hemicellulose is a gradual process during acid hydrolysis

treatment in which long polymers are gradually degraded to oligosaccharides and

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finally monosaccharide. The oligosaccharides are rather short-lived (Lee et al.,

1999), and very often they are not analyzed. The liquid phase, containing the

monosaccharide, is removed between the treatments, thereby avoiding degradation of

the monosaccharide formed. Avoiding degradation of monosaccharide is important,

not only to improve the yield, but also to avoid inhibition problems, since the

degradation products are toxic to the fermenting microorganisms (Taherzadeh et al.,

2000; Larsson et al., 1999).

Acid hydrolysis process was developed to use less severe condition to

achieve high xylan to xylose conversion yields. Achieving high xylan to xylose

conversion yield is necessary to achieve favorable overall process economics

because xylan accounts for up to a third of the total carbohydrate in many

lignocellulosic materials. It was also reported that the amount of sugar released

during hydrolysis depend on the type of raw material and operating condition of the

experiment. As a consequence, the amount of sugars recovered from the raw material

is dependent on the reaction time, temperature and acid concentration (Pessoa et al.,

1996). According to Neureiter et al., (2002), acid concentration was the most

important parameter affecting sugar yield, while for the formation of sugar

degradation products, temperature had the highest impact. Normally, dilute acid

hydrolysis was carried out at temperature between 120 oC and 200 oC.

2.3.1 Inhibitors

Hydrolysis process of hemicellulosic fraction produced pentose sugar mainly

xylose and arabinose. However, this also results in the formation of inhibitory

degradation by-products such as acetic acid, furfural and hydroxylmethylfurfural.

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The amount and nature of inhibiting compounds depend on the raw material, the

hydrolysis procedure and the reaction time in the hydrolysis process (Olsson and

Hahn-Hagerdal, 1996).

Leonard and Hajny (1945) reported that there are four classes of inhibitors

which are:

1. minerals and metals that contain in lignocellulosic materials or resulting

from the corrosion of the hydrolysis equipment

2. product derived from the hydrolysis of hemicellulose such as acetic acid,

furfural and hydroxymethylfurfural

3. product derived from lignin degradation such as phenolic compound,

aromatic acid and aldehydes and

4. compounds derived from extractives such as vanillic, syringic, caproic

and palmitic acid

Inhibitors contained in lignocellulose hydrolyzates could limit the

consumption of the carbon source, reduced the growth kinetic, or even hinder the

fermentation process. Occasionally, inhibition was a result of synergistic effects. The

direct neutralization of neutralized hydrolyzates (without further processing) usually

reduced the efficiency of fermentation, both the growth and the product formation

being affected (Frazer and McCaskey, 1989; Olsson and Hahn-Hagerdal, 1996).

Acetic acid (CH3COOH) was released from the hydrolysis of the acetyl group

in the hemicellulose, as a consequence of deacetylation of acylated pentosan

(Taherzadeh, 1999). Since acid was not further hydrolyzed, the formation of acetic

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acid depends on temperature and pressure of dilute acid hydrolysis until the acetyl

group was fully hydrolyzed. Its inhibitory action depends on the concentration of the

undissociated form, which was a function of both concentration and pH. At acidic

pH, acetic acid can diffuses into cell cytoplasm, where it dissociates and lower the

intracellular pH, resulting in uncoupled energy production and impaired transport of

various nutrients with increased ATP requirement. Acetic acid interference results in

an increased in the ATP required for this maintenance function, as well as interferes

with the cell morphology. Lawford and Rousseau (1998) reported that acetic acid

toxicity is related to the ability of undissociated (protonated) weak acid (pKa= 4.75)

to transverse the cell membrane and to act as a membrane protonophore, which

causes acidification of the cytoplasm.

Based on previous study on the bioconversion of xylose to xylitol, employing

C. guilliermondii FTI20037 cultivated in semi synthetic medium revealed that the

acetic acid concentration determined its degree to toxicity, since a concentration as

low as 1.0 g/L favoured the bioconversion, while the concentration higher than 3.0

g/L inhibited xylose consumption and xylitol formation. Studying the inhibitory

effect of acetic acid (6 g/L) using a synthetic medium containing xylose, and found

that the xylitol yield was 0.66 g/g with a volumetric productivity of 0.38 g/L/h

(Felipe et al., 1995).

Furfural and hydroxymethylfurfural were also released in the hydrolyzate

from hexose degradation causing delayed of the fermentation process or ultimate

death of the organism (Figure 2.5). Furfural has been shown to reduce the specific