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CULTIVATION OF MICROALGAE USING PALM OIL MILL EFFLUENT FOR LIPID PRODUCTION ERISA VIONY PUTRI A thesis submitted in fulfilment of the requirements for the award the degree of the Master of Engineering (Environmental) Faculty of Civil Engineering Universiti Teknologi Malaysia July 2012
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CULTIVATION OF MICROALGAE USING PALM OIL MILL EFFLUENT

FOR LIPID PRODUCTION

ERISA VIONY PUTRI

A thesis submitted in fulfilment of the

requirements for the award the degree of the

Master of Engineering (Environmental)

Faculty of Civil Engineering

Universiti Teknologi Malaysia

July 2012

iii

To my lovely husband

Reski Mai Candra

Very thankfull and grateful of the strong support.....

To my beloved parents ibu and ayah,

Roslaini and Syamsuri

Thanks for your valuable sacrifice and compassion.....

To my dearest sister and brother

Efni Uslinda, Efrizal Hendri, Eva Mardiyah, Efniza Sulsiyah, Elfi Mulziyah

To my brother in law : Bahrul Anif, Donni, Eko Widianto

To my cute nephew and niece : Fawwaz, Haziq and Najwa

Thanks for your support and always there for me in happiness and sadness.

I am very proud to have all of you

~~~~~ Love you all ~~~~

iv

ACKNOWLEDGEMENTS

I would like to thank to Allah SWT for blessing me with excellent health and

ability during the process of completing my thesis.

Special thanks go to my supervisor Dr. Mohd Fadhil Md Din and co-

supervisor Dr. Zubair Ahmed, Dr. Haryati Jamaluddin, whose gave me the

opportunity learns a great deal knowledge, so i could fulfil this achievement.

I would also like to thank the people within the “Environmental Laboratory”

and “Biological Bioscience Laboratory” whose gave me the opportunity and

friendship as long as doing experiments.

I like to express my thanks to IPASA staff, researchers, academic and

technicians that were involved in this project, and also friendship.

I would like to thank and Research Management Centre (RMC), Universiti

Teknologi Malaysia (UTM), for the financial and management support provided

under VOT 79387 (E-Science Fund) to carry out this research.

Finally, I would also like to thank all my friends in postgraduate room, in

Kolej Tun Fatimah H-25 and my colleagues for support and assistance in various

occasions. All your kindness would not be forgotten.

v

ABSTRACT

Microalgae are reported as the potential resources to produce lipid from theirbiomass cell. Lipid is generally a group of organic compound that important asprimary biofuel raw material, and also as component for foods, cosmetic products,fertilizers, animal feed, etc. As the resources of lipid production from syntheticmedia are costly, therefore the derivation of cheap sources from waste is useful inmassive scale. Therefore, the study is emphasized on the effectiveness of industrialwastewater such as palm oil mill effluent (POME) as main carbon source to maintainthe growth of microalgae and simultaneously increase the lipid content. In addition,glucose (C6H12O6) is also used to compare the effectiveness of their cultivations.Furthermore, investigation of five selected strains of green microalgae are appliednamely Chlorella vulgaris (Korean Collection for Type Cultures (KCTC) BiologicalResource Center (BRC)), Chlorella pyrenoidosa (POME), Chlorella sorokiniana(UTEX 1602), Botryococcus sudeticus (UTEX 2629), and Tetraselmis sp (UTEX2767). All cultivation of microalgae were initially carried out in 250 mL erlenmeyerflask containing 100 mL medium under ± 30oC of temperature with continuousillumination (± 14 µmol/m2/s) and up to 20 days of cultivations. The studydemonstrated that Chlorella sorokiniana, is the predominant species for specificgrowth rate (µ), biomass productivity and lipid content in diluted POME with thevalue 0.099/day, 8.0 mg/L.day, 2.68 mg lipid/mg Cell Dry Weight (CDW),respectively. However, Chlorella sorokiniana showed that there was about one andhalf times more lipid productivity when the biomass cells utilized C6H12O6 as carbonsource, compared to POME. The optimization condition was determined withvarious carbon-to-total nitrogen (C:TN) ratio and light/dark (L:D) cycles,respectively. As a result, the highest lipid content achieved when the conditioncontrolled at C:TN (100:7) and continuous light duration (24 hr), with recorded valueof 17 mg lipid/mg CDW. These results conclude that Chlorella sorokiniana hadhighest growth rates and lipid production in diluted POME compared to other strainsof microalgae. Finally, the study suggested several improvement of the experimentto achieve higher lipid production at steady - state condition by manipulating theratio of carbon-to-total nitrogen and the medium of light intensity.

vi

ABSTRAK

Mikroalga dilaporkan sebagai sumber yang berpotensi untuk menghasilkanlipid daripada sel biojisim. Lipid secara umumnya merupakan satu kumpulansebatian organik yang penting sebagai bahan mentah utama biofuel, dan juga sebagaikomponen untuk makanan, kosmetik, produk baja, pemakanan haiwan, dan lain -lain. Sumber penghasilan lipid daripada media sintetik adalah mahal, oleh kerana itupenghasilan sumber yang murah daripada sisa bahan buangan adalah berguna untukskala yang besar. Kajian ini memberi penekanan kepada kesan air sisa industriseperti buangan kilang kelapa sawit (POME) sebagai sumber karbon yang utamauntuk mengekalkan pertumbuhan mikroalga dan meningkatkan kandungan lipid. Disamping itu, glukosa (C6H12O6) digunakan sebagai perbandingan pengkulturan yangberkesan. Selain itu, lima jenis mikroalga hijau yang dipilih untuk kajian adalahseperti Chlorella vulgaris (Koleksi dari Korea untuk jenis kultur (KCTC), PusatSumber Biologi (BRC), Chlorella pyrenoidosa (POME), Chlorella sorokiniana(UTEX 1602), Botryococcus sudeticus (UTEX 2629) dan Tetraselmis sp (UTEX2767). Semua pengkulturan mikroalga dilakukan di dalam 250 mL kelalang yangmengandungi 100 mL medium di bawah suhu kawalan ± 30oC dengan pencahayaanyang berterusan (± 14 µmol/m2/s) dan dikultur sehingga 20 hari. Kajian inimenunjukkan bahawa Chlorella sorokiniana adalah spesies yang berpotensi danpaling dominan kerana ia mencatatkan bacaan yang lebih baik untuk kadarpertumbuhan tertentu (µ), biojisim, dan kandungan lipid dalam cairan POME dengannilai yang direkodkan masing – masing sebanyak 0.099/hari, 8.0 mg/L.hari dan 2.68mg lipid/mg berat kering sel (CDW). Namun, Chlorella sorokiniana mempunyaiproduktiviti lipid kira - kira satu setengah kali lebih apabila sel – sel biojisimmenggunakan C6H12O6 sebagai sumber karbon, berbanding POME. Keadaan yangoptimum didapati sebagai variasi nisbah karbon terhadap pelbagai jumlah nitrogendan cahaya/gelap (L:D) kitaran, masing – masing. Hasilnya, kandungan lipidtertinggi diperolehi pada keadaan yang dikawal C:TN (100:7) dan pencahayaan yangberterusan dengan nilai sebanyak 17 mg lipid/mg CDW. Keputusan inimenunjukkan bahawa pertumbuhan Chlorella sorokiniana mempunyai kadarpertumbuhan dan pengeluaran lipid tertinggi dalam POME yang dicairkan, jikadibandingkan dengan jenis mikroalga yang lain. Akhir sekali, kajian inimencadangkan beberapa penambahbaikan untuk menjalankan eksperimen bagimencapai penghasilan lipid yang lebih tinggi pada keadaan stabil denganmemanipulasikan nisbah karbon kepada jumlah nitrogen dan keamatan cahaya yangsederhana.

vii

TABLE OF CONTENTS

CHAPTER TITLE PAGE

DECLARATION ii

DEDICATION iii

ACKNOWLEDGEMENTS iv

ABSTRACT v

ABSTRAK vi

TABLE OF CONTENTS vii

LIST OF TABLES xi

LIST OF FIGURES xiii

LIST OF ABBREVIATIONS xv

LIST OF SYMBOLS xvii

LIST OF APPENDICES xviii

1 INTRODUCTION

1.1 Background of the Study 1

1.2 Problem Statement 2

1.3 Objectives of the Study 3

1.4 Scope of the Study 4

1.5 Significance of the Study 4

2 LITERATURE REVIEW

2.1 History of Microalgae 6

2.2 Microalgae Divisions 7

2.3 Cultivation Conditions of Microalgae 10

viii

2.3.1 Phototrophic Cultivation 10

2.3.2 Heterotrophic Cultivation 15

2.3.3 Mixotrophic Cultivation 16

2.3.4 Photoheterotrophic Cultivation 17

2.4 Culture Parameters 17

2.4.1 Environmental Condition 18

2.4.1.1 Light Intensity 18

2.4.1.2 pH 18

2.4.1.3 Temperature 19

2.4.1.4 Mixing 20

2.4.1.5 Salinity 20

2.4.2 Nutrients 21

2.4.2.1 Carbon Sources 21

2.4.2.2 Phosphorus 21

2.4.2.3 Nitrogen 22

2.4.2.4 Other Elements 22

2.5 Growth Cycle of Microalgae 23

2.5.1 Lag Phase 24

2.5.2 Exponential Growth Phase 24

2.5.3 Deceleration Growth Phase 26

2.5.4 Stationary Phase 26

2.5.5 Death Phase 27

2.6 Maintenance of Growth 27

2.7 Importance of Microalgae 28

2.7.1 Microalgae as Feedstock for Biodiesel 28

2.7.2 Lipid Production from Microalgae 31

2.8 Microalgae Versus Wastewater 32

2.8.1 Microalgae Growth in Municipal Sewage

Wastewater

36

2.8.2 Microalgae Growth in Agricultural

Wastewater

36

2.8.3 Microalgae Growth in Artificial

Wastewater

37

ix

2.8.4 Microalgae Growth in Industrial

wastewater

38

2.9 Wastewater from Palm Oil, POME 38

2.9.1 Characteristic of POME 39

2.9.2 POME as Nutrients Source to Culture

Microalgae

40

3 RESEARCH METHODOLOGY

3.1 Introduction 46

3.2 Material and Methods 48

3.2.1 Preparation of the Inoculumns 48

3.2.2 Wastewater Collection 51

3.2.3 Antibiotic Preparation 52

3.3 Types of Experimental Parameters 53

3.3.1 Optical Density 53

3.3.2 Chlorophyll a Content 54

3.3.3 Chemical Oxygen Demand 55

3.3.4 Total Nitrogen Measurements 55

3.3.5 Mixed Liquor Suspended Solids and

Mixed Liquor Volatile Suspended Solids

55

3.3.6 Cell Dry Weight 56

3.3.7 Lipid Extraction 57

3.4 Experimental Procedure 58

3.4.1 Preliminary Study (selection of suitable

concentration of microalgae)

58

3.4.2 Selection of Suitable Strain (First Set up) 59

3.4.3 Comparison POME and Glucose as Sole

Carbon Source

61

3.4.4 Optimization Lipid Content 61

3.5 Inhibition Model 62

3.6 Kinetic and Yield Parameter 63

x

4 RESULT AND DISCUSSION

4.1 Preliminary Study in The Settled POME 64

4.1.1 Effect of Substrate 65

4.1.2 Substrate Consumption Rate 66

4.1.3 Growth Rate of Microalgae 68

4.1.4 Biomass Productivity 69

4.1.5 Inhibition Model 71

4.2 Investigation of Microalgae for High Lipid

Content Using POME as Carbon Source

73

4.2.1 Microalgae Growth 73

4.2.2 Lipid Content Analysis 75

4.2.3 Carbon Source Consumption 78

4.3 Cultivation of Chlorella Sorokiniana Using

POME and Glucose as Carbon Source

79

4.4 Chlorella Sorokiniana From Settled Raw Palm

Oil Mill Effluent (POME) for Lipid Production

83

4.4.1 Correlation of Organic Carbon Substrate

and Nutrient Utilization Rate

83

4.4.2 Relationship of Organic Carbon and

Nutrient Utilization with Lipid Production

by Microalgae

86

4.5 Effect of Photo Cycles (light : dark) on Lipid

Production by Chlorella Sorokiniana in POME

88

5 CONCLUSION

5.1 Conclusion 91

5.2 Recommendation 92

REFERENCES 94

Appendices A - B 102 - 108

xi

LIST OF TABLES

TABLE NO. TITLE PAGE

2.1 The main pigments, storage products, and cell coverings

of the algal divisions (Barsanti and Gualtieri, 2006)

8

2.2 The lipid content and productivities of different

microalgae species under different cultivation condition

(Chen et al., 2011)

11

2.3 Comparison of some source of biodiesel (Chisti, 2007) 29

2.4 Oil content of microalgae (Chisti, 2007, Khan et

al., 2009, Lam and Lee, 2011)

30

2.5 Biomass productivity, lipid content and lipid productivity

of 30 microalgae strains cultivated in 250 mL flask

(Rodolfi et al., 2009)

33

2.6 The growth of microalgae under a variation of wastewater

condition (Pittman et al., 2011)

35

2.7 Characteristic of POME (Wong et al., 2009) 40

2.8 Summarizes of previous study about types of microalgae

using in any kind of wastewater

42

3.1 Strain of Microalgae 48

3.2 Bolds Basal Medium (BBM) (Barsanti and Gualtieri,

2006)

49

3.3 Soil Extract Medium 50

3.4 Modified Bold 3N Medium 50

xii

3.5 Characteristic of the sampled POME 52

4.1 COD consumption by Chlorella vulgaris under different

concentrations of POME at 28 days

67

4.2 Value of µ and R2 for every substrate concentration by

Chlorella vulgaris

69

4.3 Results of growth and biomass productivity of microalgae

in appropriate medium

73

4.4 Maximum value for specific growth rate, carbon source

consumption, chlorophyll productivity, biomass

productivity and ratio MLVSS/MLSS

82

4.5 Comparison of nitrogen utilization by Chlorella

sorokiniana

85

xiii

LIST OF FIGURES

FIGURE NO. TITLE PAGE

2.1 Typical growth curve for microorganism population (Bitton,

1994)

23

2.2 Chemostat for continuous culture of microorganism (Bitton,

1994)

28

3.1 Steps in the experimental operation 47

3.2 Facultative Ponds 51

3.3 Replicates of antibiotic (Chloramphenicol) Preparation 53

3.4 Optical density measurement at wavelength 600 nm 54

3.5 Sample on freeze dryer 57

3.6 Microalgae cells after have done for extraction 58

3.7 Chlorella vulgaris cultivation in different COD concentration 59

3.8 Flask set up used for all microalgae strains 60

3.9 Light intensity measurement using Lux Meter 61

4.1 Initial with final COD removal in different POME

concentration for Chlorella vulgaris

66

4.2 Variation of substrate consumption with the operation time by

Chlorella vulgaris

67

4.3 Growth rate of microalgae under different initial substrate 68

xiv

concentration by Chlorella vulgaris

4.4 Variation of the Napierian logarithm of the quotient between

the MLSS concentrations at any time by Chlorella vulgaris

70

4.5 Variation of the Napierian logarithm of the quotient between

the MLVSS concentrations at any time by Chlorella vulgaris

70

4.6 Comparison of the model values and experimental data, A

(MLSS measurements), B (MLVSS measurements ), C (OD

measurements) by Chlorella vulgaris performance

72

4.7 Chlorophyll content for five strain of microalgae in batch

culture

74

4.8 Changes of green color for types of microalgae in 20 days 75

4.9 Percentage of lipid content for types of microalgae 76

4.10 Lipid content for five strain of microalgae in batch culture 76

4.11 Correlation of lipid content with MLVSS and chlorophyll

content during of batch culture

77

4.12 Chlorophyll production of microalgae based on carbon

sources consumption

79

4.13 Comparison of biomass between POME and C6H12O6 during

of experiment

80

4.14 Relationship of MLSS with chlorophyll content using POME

and C6H12O6

80

4.15 Comparison of ratio MLVSS/MLSS and lipid content for

POME and C6H12O6 in batch culture

82

4.16 Organic carbon substrate rates during of experiment 84

4.17 Utilization rate of nutrients during of experiment 85

4.18 Relationship between organic carbon substrate rate profile and

specific growth rate (Note: A = most of experiment

conducted, B = lipid production potentially)

86

4.19 (A) Relationship lipid productivity and nutrient utilization

rate, (B) relationship lipid productivity and organic carbon

substrate

87

xv

4.20 The effect of light/dark cycles on specific growth rate profiles 88

4.21 Lipid productivity for three light/dark cycles during of

cultivation

89

4.22 Relationship of chlorophyll production rate and lipid

productivity in varying light/dark cycles

90

xvi

LIST OF ABBREVIATION

ATP - Adenosine Triphosphate

BBM - Bolds Basal Medium

BOD - Biochemical Oxygen Demand

B. sudeticus - Botryococcus sudeticus

C. sorokiniana - Chlorella sorokiniana

C. pyrenoidosa - Chlorella pyrenoidosa

C. vulgaris - Chlorella vulgaris

C : TN - Carbon to total nitrogen ratio

Ca - Calcium

CDW - Cell Dry Weight

cells/mL - Cell per mili liter

CO2 - Carbon dioxide

COD - Chemical Oxygen Demand

DNA - Deoxyribonucleic Acid

Fe - Ferrite

g/L - Gram per liter

H2O - Hidrogen Oxide

H2PO4- - Dihydrogen Phosphate Ion

HPLC - High-Performance Liquid Chromatography

HPO42- - Hydrogen Phosphate Ion

K - Kalium

kJ/g - Kilo Joule per gram

L: D - Light : dark

Mg - Magnesium

mg/L/day - Mili gram per liter per day

xvii

MLSS - Mixed Liquor Suspended Solid

MLVSS - Mixed Liquor Volatile Suspended Solid

N - Nitrogen

NADP+ - Nicotinamide Adenine Dinucleotide Phosphate

NH4+ - Ammonium

NO2- - Nitrite

NO3- - Nitrate

OD - Optical Density

P - Phosphorus

POME - Palm Oil Mill Effluent

R2 - Variance accounted

RNA - Ribonucleic Acid

So - Substrate concentration

Topt - Temperature optima

TAGs - Triacylglycerols

TSS - Total Suspended Solids

VSS - Volatile Suspended Solids

Zn - Zinc

xviii

LIST OF SYMBOLS

µ - specific growth rate

µm - maximum specific growth rate

A - weight of filter +dried residue

B - weight of filter

C - weight of residue + dish before ignition

D - weight of residue + dish or filter after ignition

e - exponential

Ki - dissociation constant

Ks - half saturation constant

L - width of cuvette

t - time

τd - doubling time of cell mass

τ'd - doubling time based on the replication rate

V1 - volume of extract

V2 - volume of sample

X - concentration at beginning

X’ - growth of microalgae concentration

X’0 - value of growth concentration

X0 - concentration at beginning

α - alpha

β - beta

γ - gamma

ε - epsilon

xix

LIST OF APPENDICES

APPENDIX TITLE PAGE

A CONVERSION : PPF TO LUX

EXPERIMENTAL DATA

102

B 103

CHAPTER 1

INTRODUCTION

1.1 Background of the Study

Nowadays, palm oil industry is growing rapidly and becoming a significant

agriculture-based industry in Malaysia. The number of palm oil mills has increased

tremendously, at starting with 10 mills in 1960 climbed to 410 operated mills in

2008. At least 44 million tones of POME was generated and are expected to rise

every year in Malaysia (Wu et al., 2010), particularly because of the initiative of the

government to promote palm oil industry. Furthermore, it is necessary to proper

address in Palm Oil Mill Effluent (POME) treatment so as not contribute to human

health hazards and environmental pollution.

Small scale and economically viable technologies that combine wastewater

treatment and energy production can treat the industrial effluents and enhance the

availability of the energy simultaneously (Lansing et al., 2008). The feasible way

that is more attentions in the present time is the use of microalgae, which is known to

have the potential to treat wastewater (Tarlan et al., 2002) such as remove CO2 and

NOx (Jin et al., 2008), high capacity of nutrient uptake (Park, 2009). The idea of

2

using microalgae in wastewater treatment has been investigated since 1950s, by

Oswald (1957).

Microalgae appear to be an attractive renewable energy source especially for

biodiesel production (Travieso et al., 2006; Chisti, 2007; Griffiths and Harrison,

2009; Converti et al., 2009; Gao et al., 2010; Feng et al., 2011). Its due to their have

rapid growth rate: 100 times faster than land based plant and they can double their

biomass in less than a day. Furthermore, microalgae are able to divide once every 3-

4 h, but mostly divide every 1-2 days under favorable growing conditions (Griffiths

and Harrison, 2009; Huang et al., 2010; Lam and Lee, 2011).

Actually, the interest in microalgae for biodiesel production is due to the high

lipid content of some species, and to the fact that lipid synthesis, especially of the

non-polar TAGs (triacylglycerols), which are the best substrate to produce biodiesel,

can be modulated by varying growth conditions. The total content of lipids in

microalgae may vary from about 1–85% of the dry weight, with values higher than

40% being typically achieved under nutrient limitation. Moreover, view of factors

such as temperature, irradiance and, most markedly, nutrient availability have been

shown to affect both lipids composition and content in many microalgae (Rodolfi et

al., 2009).

1.2 Problem Statement

Because agro-industrial wastewater consist of large amounts of organic

compounds and heavy metals are hazardous to environmental health, microalgae

have been suggested as very good candidate to remove these pollutants and

breakdown the organic compounds present (Munoz and Guieysse, 2006).

3

On the other hand, culturing microalgae in wastewater offers an inexpensive

alternative to conventional forms of wastewater treatments. At the same time

microalgae can utilize the nitrogen and phosphorus compound in wastewater to

generate microalgae biomass for lipids production as well as biofuel production

(Huang et al., 2010). Moreover, since the late 1900’s, the fuel have been

tremendously used for transportation, power plants, heating, and cosmetics, then

increasing fossil fuel prices and the contribution of petroleum to air pollution make

fossil fuel untenable as the predominant source of energy.

Therefore, an alternative of energy and fuel source, especially from the

renewable resource could make us be less dependent on the conventional fuel energy.

Hence, microalgae come up as alternative technologies to resolve this problem. This

study was undertaken with the aim to evaluate the potential of POME as carbon

source for microalgae to produce high lipid.

1.3 Objectives of the Study

i. To identify a suitable strain of microalgae species, which could effectively

grows in POME.

ii. To compare the ability of microalgae species growth and survive in POME

and glucose as carbon sources.

iii. To quantify the lipid content from suitable microalgae based on optimum

condition of carbon to total nitrogen ratio (C: TN), and cultivation period.

4

1.4 .Scope of the Study

The study is to emphasize on the production of microalgae using POME as

substrate with varying operating parameter (e.g optical density (OD), Chlorophyll

content, Mixed Liquor Suspended Solid (MLSS), Mixed Liquor Volatile Suspended

Solid (MLVSS), and Cell Dry Weight (CDW)). POME was collected from

facultative ponds in Kahang Palm Oil Mill, Johor Bahru, Malaysia. This study start

under different concentration, i.e. 0, 250, 500, 1000 mg COD/L with Chlorella

vulgaris applied.

The appropriate concentration would be used in subsequent experiments.

First, to investigate five strain of green microalgae such as Chlorella sorokiniana,

Chlorella pyrenoidosa, Botryococcus sudeticus, Tetraselmis sp and also Chlorella

vulgaris, which were detected as high lipid content. Next, comparison between

POME and glucose as carbon source has been identified to examine the effect of

mixed carbon compound for the specific growth rate (µ) of microalgae. Finally,

optimization of lipid content from chosen microalgae strain based on suitable

conditions including, carbon to total nitrogen ratio and photo light period have been

investigated.

1.5 Significance of the Study

A number of researchers used wastewater as growth medium for microalgae

cultivation, biomass productivity and test the capability of microalgae to remove

nitrate, reduce levels of phosphate, ammonium and nitrate. Kind of wastewater

commonly used comes from domestic wastewater, municipal wastewater,

agricultural wastewater, artificial wastewater and industrial wastewater.

5

Furthermore, culturing microalgae in wastewater offers an inexpensive

alternative to conventional forms of biological wastewater treatments and at the same

time to utilize the nitrogen and phosphorus compounds in wastewater. Here, this

study is employing industrial wastewater comes from palm oil mill effluent in order

to evaluate the potential of microalgae growth, biomass productivity, and lipid

production. Therefore, the study is significant to prove that POME as potential

carbon source for microalgae growth in producing lipid, which are useful for finding

an alternative energy and fuel source particularly from the renewable sources.

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