PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE...

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PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE VIRGIN COCONUT OIL OVER HZSM-5 ZEOLITE BY MISS PANADDA YOTSOMNUK A THESIS SUBMITTED IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF MASTER DEGREE OF ENGINEERING (CHEMICAL ENGNEERING) DEPARTMENT OF CHEMICAL ENGINEERING FACULTY OF ENGINEERING THAMMASAT UNIVERSITY ACADEMIC YEAR 2017 COPYRIGHT OF THAMMASAT UNIVERSITY Ref. code: 25605810030592YLH

Transcript of PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE...

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PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE VIRGIN COCONUT OIL OVER HZSM-5 ZEOLITE

BY

MISS PANADDA YOTSOMNUK

A THESIS SUBMITTED IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF MASTER DEGREE OF ENGINEERING

(CHEMICAL ENGNEERING) DEPARTMENT OF CHEMICAL ENGINEERING FACULTY OF ENGINEERING

THAMMASAT UNIVERSITY ACADEMIC YEAR 2017

COPYRIGHT OF THAMMASAT UNIVERSITY

Ref. code: 25605810030592YLH

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PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE VIRGIN COCONUT OIL OVER HZSM-5 ZEOLITE

BY

MISS PANADDA YOTSOMNUK

A THESIS SUBMITTED IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF MASTER DEGREE OF ENGINEERING

(CHEMICAL ENGINEERING) DEPARTMENT OF CHEMICAL ENGINEERING FACULTY OF ENGINEERING

THAMMASAT UNIVERSITY ACADEMIC YEAR 2017

COPYRIGHT OF THAMMASAT UNIVERSITY

Ref. code: 25605810030592YLH

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Thesis Title PRODUCTION OF BIOFUEL BY

HYDROCONVERSION OF WASTE VIRGIN

COCONUT OIL OVER HZSM-5 ZEOLITE

Author Miss Panadda Yotsomnuk

Degree Master of Engineering

Major Field/Faculty/University Chemical Engineering

Faculty of Engineering

Thammasat University

Thesis Advisor Associate Professor Wanwisa Skolpap, Ph.D.

Academic Years 2017

ABSTRACT

This research aimed to determine the influence of process parameters on

yields of biofuel production by hydroconversion of waste virgin coconut oil using

HZSM-5 zeolite catalyst and to determine statistical relationship of biofuel yields with

the operating parameters program by Pearson’s correlation. The hypothesis of this

research was tested at 95% confidence level. The various operating parameters in

batch reactor were a reaction temperature (350-400°C), an initial hydrogen pressure

(20-40 bar), and a reaction time (1-3 h). The reaction products were then separated by

distillation. The highest yields of gasoline (6.79 wt%) and kerosene (31.38 wt%) were

achieved under a temperature at 400°C, initial hydrogen pressure at 40 bar, and a

reaction time of 3 h. The highest yield of diesel of 58.62 wt% was achieved at a reaction

time of 1 h under temperature 400°C and initial hydrogen pressure 40 bar. The

experimental data were analyzed by input-output model with the coefficient of

determination (R2) of yield prediction ranging from 0.86 to 0.92. The Pearson’s

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correlation coefficients show strong dependence of reaction temperature and time on

hydrocarbon chains of various length. Yields of shorter hydrocarbon chains such as

biogasoline and biokerosene required higher reaction temperature and longer reaction

time and vice versa. Pressure dependence on yields of biofuels was insignificant.

Keywords: Virgin coconut oil, Zeolite, HZSM-5, Hydroconversion

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หวขอวทยานพนธ การผลตเชอเพลงเหลวดวยกระบวนการไฮโดรคอนเวอรชนจากการแปรรปของเสยจากกระบวนการผลตนามนมะพราวบรสทธโดยอาศยตวเรงปฏกรยาซโอไลต HZSM-5

ชอผเขยน นางสาวปนดดา ยศสมนก ชอปรญญา วศวกรรมศาสตรมหาบณฑต สาขาวชา/คณะ/มหาวทยาลย วศวกรรมเคม

วศวกรรมศาสตร มหาวทยาลยธรรมศาสตร

อาจารยทปรกษาวทยานพนธ รองศาสตราจารย ดร. วนวสาข สกลภาพ ปการศกษา 2560

บทคดยอ

งานวจยนมวตถประสงคเพอศกษาอทธพลตวแปรกระบวนการไฮโดรคอนเวอรชนโดยใชตวเรงปฏกรยาซโอไลต HZSM-5ทมตอคาผลไดในการผลตเชอเพลงชวภาพจากนามนเหลอทงจากกระบวนการผลตนามนมะพราวบรสทธ และเพอหาความสมพนธเชงสถตระหวางคาผลไดและตวแปรศกษาดวยสหสมพนธของเ พยรสน (Pearson’s correlation) ตวแปรกระบวนการท ศ กษากระบวนการไฮโดรคอนเวอรชนในเครองปฏกรณชวภาพตนแบบขนาดเลก แบบกะ ไดแกอณหภมในการทาปฏกรยาไฮโดรคอนเวอรชนท 350-400 องศาเซลเซยส, ความดนไฮโดรเจนเรมตนท 20-40 บาร และเวลาในการทาปฏกรยาท 1-3 ชวโมง ผลตภณฑเชอเพลงชวภาพในสวนของของเหลวถกวเคราะหโดยการกลน จากผลการทดลองพบวา ผลผลตสงสดของนามนไบโอเคโรซนและนามนไบโอแกสโซลนสงสดท 31.38 เปอรเซนตโดยนาหนก และ 6.79 เปอรเซนตโดยนาหนก ตามลาดบ ภายใตสภาวะอณหภม 400 องศาเซลเซยส ความดนไฮโดรเจนเรมตนท 40 บารและเวลาในการทาปฏกรยา 180 นาท และผลผลตสงสดของนามนดเซลอยท 58.62 รอยละโดยนาหนก ทอณหภม 350 องศาเซลเซยส ความดนไฮโดรเจนเรมตนท 40 บารและเวลาในการทาปฏกรยา 60 นาท จากนนทดสอบเปรยบเทยบความสมพนธระหวางผลตภณฑเชอเพลงชวภาพกบตวแปรตางๆทไดทาการศกษา โดยวเคราะหเชงสถตเพอหาคาสมประสทธสหสมพนธของเพยรสน (Pearson’s correlation) จากเมอวเคราะหขอมลการทดลองโดยใชแบบจาลองทางคณตศาสตรแบบอนพด -เอาทพต พบวาคาสมประสทธการตดสนใจ (Coefficient of determination, R2) อยในชวง 0.86-0.92 สาหรบการ

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วเคราะหเชงสถตระหวางคาผลไดและตวแปรศกษาดวยสหสมพนธของเพยรสน (Pearson’s correlation) โดยกาหนดระดบความเชอมนทรอยละ 95 พบวาความสมพนธระหวางความยาวทแตกตางกนของสายไฮโดรคารบอนทผลตได ขนกบอณหภมและระยะเวลาในการทาปฎกร ยาไฮโดรคอนเวอรชน กลาวคอ ผลตภณฑในชวงคารบอนสายโซสน เชน นามนไบโอแกสโซลนและนามนไบโอเคโรซน ใหคาผลไดสงทอณหภมสงและระยะเวลาในการเกดปฎกรยาทนาน สาหรบอทธพลความดนไฮโดรเจนไมมผลตอคาผลไดของผลตภณฑนามนเชอเพลงอยางมนยสาคญ ค ำส ำคญ: นามนมะพราวสกดเยน, ซโอไลต, HZSM-5, ไฮโดรคอนเวอรชน

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ACKNOWLEDGEMENTS

This thesis would have been impossible without the help from my advisor,

Assoc. Prof. Dr. Wanwisa Skolpap. Apart from academic support, Assoc. Prof. Dr.

Wanwisa Skolpap gave significant advice for improving my research skill. Furthermore,

she taugh me the way to live as my parents did, and gave me the education

opportunity including financial support during my study.

Besides, I would like to express my thanks to the committee including

Assoc. Prof. Dr. Nurak Grisadanurak, Assoc. Prof. Dr. Attasak Jaree, Asst. Prof. Dr.

Suwadee Kongparakul for valuable recommendations to improve quality of my thesis.

Moreover, I am deeply grateful to my family for encouragement and their

continued prayer and moral support through the course of my graduate studies. Many

thanks also for all my friends who are always very helpful and supporting.

Finally, I would like to thank Faculty of Engineering, Thammasat University

for the scholarship and gratefully acknowledge the financial support provided by

Thammasat University Research Fund

Miss Panadda Yotsomnuk

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TABLE OF CONTENTS

Page

ABSTRACT (1)

ACKNOWLEDGEMENTS (5)

LIST OF TABLES (10)

LIST OF FIGURES (13)

CHAPTER 1 INTRODUCTION 1

1.1 Background 1

1.2 Objectives 3

1.3 Scope 3

1.4 Expected output 4

CHAPTER 2 LITERATURE REVIEW 5

2.1 Vegetable oil 5

2.1.1 Coconut oil 8

2.1.2 Virgin coconut oil 9

2.2 Hydrocracking 11

2.2.1 Hydrocracking catalyst 13

2.3 Zeolite 13

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2.3.1 The structure of zeolite 14

2.3.2 Shape selectivity 16

2.3.3 ZSM-5 17

2.4 Parameter condition

2.4.1 Effect of initial hydrogen pressure

2.4.2 Effect of reaction temperature

2.4.3 Effect of reaction time

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CHAPTER 3 RESEARCH METHODOLOGY 28

3.1 Chemical and reagents 28

3.2 Methodology 31

3.2.1 Preparation of HZSM-5 zeolite 32

3.2.2 Characterization of zeolite 32

3.2.2.1 X-ray powder diffraction 32

3.2.2.2 Scanning electron microscopy 33

3.2.2.3 Temperature programmed desorption 33

3.2.2.4 Gas Chromatography-Mass Spectrometry 33

3.3 Hydrocracking process 33

CHAPTER 4 RESULTS AND DISCUSSION 37

4.1 Characterization Analysis 37

4.1.1 X-ray powder diffraction 37

4.1.2 Scanning electron microscopy 38

4.1.3 Temperature programmed desorption 40

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4.2 Effect of operating parameters on hydrocracking of waste

virgin coconut oil

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4.2.1 Effect of initial hydrogen pressure 40

4.2.2 Effect of reaction temperature 43

4.2.3 Effect of reaction time 45

4.3 Data analysis from the input-output model 48

4.4 Accuracy of models used in liquid biofuel yield prediction

4.5 Data analysis – Pearson’s correlation coefficient

4.6 The reaction product distribution

4.6.1 The number of carbon atom

4.6.2 Selectivity of kerosene range hydrocarbon

4.7 Degree of deoxygenation (DOD) and degree of cracking (DOC)

4.7.1 Effect of reaction parameters on the degree of

deoxygenation (DOD) and degree of cracking (DOC) in the

batch reactor

4.8 Continuous process

4.8.1 Experimental

4.8.2 Product Analysis

4.8.3 Effect of hydrogen flow rate

4.8.4 Effect of reaction time on catalyst activity and selectivity

to product

CHAPTER 5 CONCLUSIONS AND RECOMMENDATIONS

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5.1 Conclusion 72

5.2 Recommendations 73

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REFERENCES 74

APPENDICES 83

APPENDIX A Raw data of characterization

84

APPENDIX B Raw data of experimental results 92

APPENDIX C Calculation

APPENDIX D Pearson’s correlation

APPENDIX E Product distribution (batch reactor)

APPENDIX F The product distribution was detected by gas

chromatography (continuous reactor)

APPENDIX G The pathway of hydroprocessing process (batch process)

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BIOGRAPHY 110

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LIST OF TABLES

Tables Page

2.1 The composition of fatty acid in various types of vegetable oils

(%w/w)

6

2.2 Free fatty acid (FFA) I virgin coconut oil 10

2.3 Previous studies on the effect of initial hydrogen pressure 23

2.4 Previous studies on the effect of reaction temperature 26

2.5 Previous studies on the effect of reaction time

3.1 Analysis data of low-grade waste virgin coconut oil (WCO)

3.2 Analysis data of high-grade waste virgin coconut oil (WCO)

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4.1 Results of TPD-NH3 analysis over HZSM-5 zeolite 40

4.2 The effect of initial hydrogen pressure on conversion (Xl), yield,

and selectivity of liquid product fraction for waste virgin coconut

oil

41

4.3 The effect of reaction temperature on conversion (Xl), yield, and

selectivity of liquid product fraction for waste virgin coconut oil

43

4.4 The effect of reaction time on conversion (Xl), yield, and

selectivity of liquid product fraction for waste virgin coconut oil

46

4.5 The calculated correlation coefficients

4.6 Pearson’s correlation coefficients of yield of liquid biofuel with

initial hydrogen pressure (P), reaction temperature (T), and

reaction time (t)

A.1 Compositional analysis of low-grade waste virgin coconut oil

A.2 Compositional analysis of high-grade waste virgin coconut oil

A.3 Data of Theta and six highest peaks of zeolite and H-zeolite

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A.4 Raw data of temperature programmed desorption of ammonia

A.5 Flash point analysis

B.1 Experimental conditions

B.2 Effect of initial hydrogen pressure on product yield, selectivity

and conversion of waste virgin coconut oil cracking to biofuels

through hydrocracking process over HZSM-5 as catalyst at 400°C

and 1 h

B.3 Effect of reaction temperature on product yield, selectivity and

conversion of waste virgin coconut oil cracking to biofuels

through hydrocracking process over HZSM-5 as catalyst at 40 bar

and 1 h

B.4 Effect of reaction time on product yield, selectivity and

conversion of waste virgin coconut oil cracking to biofuels

through hydrocracking process over HZSM-5 as catalyst at 400°C

and 40 bar

D.1 Pearson’s correlation for operating parameters on gasoline

production

D.2 Pearson’s correlation for operating parameters on kerosene

production

D.3 Pearson’s correlation for operating parameters on diesel

production

D.4 Liquid biofuel yield comparison between experimental (actual)

and model predicted result

E.1 The effect of initial hydrogen pressure on the product

distribution and degree of deoxygenation and degree of cracking

E.2 The effect of reaction temperature on the product distribution

and degree of deoxygenation and degree of cracking

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E.3 The effect of reaction time on the product distribution and

degree of deoxygenation and degree of cracking

E.4 The product distribution and degree of deoxygenation and

degree of cracking at the condition no add catalyst (400°C/40

bar/60 minutes) and no add hydrogen (400°C/60 minutes)

E.5 The selectivity of carbon atom number of liquid yield from

hydrocracking process over HZSM-5 was detected by gas-

chromatography

E.6 The distribution of aromatic, alkane, and alkene for kerosene

fraction

F The effect of hydrogen flow rate (ml/min) on the selectivity to

product at the various of reaction time (°C)

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LIST OF FIGURES

Figures Page

2.1 Chemical structure of vegetable oil 7

2.2 Coconut palm 8

2.3 Virgin coconut oil 9

2.4 The possible reaction pathways 12

2.5 Structure of zeolite 14

2.6 Various types of zeolite; (a) small pore zeolites, (b) medium

pore zeolites, (c) large pore zeolites

15

2.7 Shape selectivity in zeolite channels 16

2.8 Scheme of the channel system in ZSM-5 17

2.9 Scheme for generating Bronsted and Lewis acid sites in zeolites

3.1 low-grade and high-grade waste virgin coconut oil

3.2 Experimental procedure

3.3 Scheme of HZSM-5 zeolite preparation

3.4 Schematic diagram of the batch reactor

3.5 Batch reactor

3.6 Distillation

4.1 XRD patterns of HZSM-5

4.2 SEM images of (a) (b) HZSM-5

4.3 SEM images of (c) (d) ZSM-5

4.4 EDX Spectrum

4.5 Effect of initial hydrogen pressure on liquid product fractions

(wt%) in the catalytic hydrocracking of waste virgin coconut oil

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(Conditions: Catalyst = 1 g of HZSM-5, reaction temperature =

400°C and reaction period = 1 h)

4.6 Effect of reaction temperature on liquid product fractions (wt%)

in the catalytic hydrocracking of waste virgin coconut oil

(Conditions: Catalyst = 1 g of HZSM-5, initial hydrogen pressure

= 40 bar and reaction period = 1 h)

4.7 Effect of reaction time on liquid product fractions (wt%) in the

catalytic hydrocracking of waste virgin coconut oil (Conditions:

Catalyst = 1 g of HZSM-5, initial hydrogen pressure = 40 bar and

reaction temperature = 400°C)

4.8 The input-output correlation of the effect of initial hydrogen

pressure (P)

4.9 The input-output correlation of the effect of reaction

temperature(T)

4.10 The input-output correlation of the effect of reaction time (t)

4.11 Correlation between actual and predicted yield for gasoline

4.12 Correlation between actual and predicted yield for kerosene

4.13 Correlation between actual and predicted yield for diesel

4.14 The effect of initial hydrogen pressure on the distribution of

carbon atom number of liquid products yielded from

hydrocracking process over HZSM-5

4.15 The effect of reaction temperature on the distribution of carbon

atom number of liquid products yielded from hydrocracking

process over HZSM-5

4.16 The effect of reaction time on the distribution of carbon atom

number of liquid products yielded from hydrocracking process

over HZSM-5

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4.17 The effect of reaction temperature on the selectivity for kerosene

fraction toward formation of aromatic, alkane, and alkene

4.18 The effect of initial hydrogen pressure on the selectivity for

kerosene fraction toward formation of aromatic, alkane, and

alkene

4.19 The effect of reaction time on the selectivity for kerosene fraction

toward formation of aromatic, alkane, and alkene

4.20 The effect of the reaction temperature on the degree of

deoxygenation on over HZSM-5 catalysts

4.21 The effect of the reaction temperature on the degree of cracking

on over HZSM-5 catalysts

4.22 The effect of the initial hydrogen pressure on the degree of

deoxygenation on over HZSM-5 catalysts

4.23 The effect of the initial hydrogen pressure on the degree of

cracking on over HZSM-5 catalysts

4.24 The effect of the reaction time on the degree of deoxygenation

on over HZSM-5 catalysts

4.25 The effect of the reaction time on the degree of cracking on over

HZSM-5 catalysts

4.26 Reactor set-up

4.27 Decanoic acid conversion over HZSM-5 as function of time

4.28 The effect of the hydrogen flow rate on product formation at

the reaction time 30 minutes

4.29 The effect of the hydrogen flow rate on product formation at

the reaction time 60 minutes

4.30 The effect of the hydrogen flow rate on product formation at

the reaction time 90 minutes

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4.31 The effect of a reaction time with the hydrogen flow rate 50

ml/min

4.32 The effect of hydrogen flow rate on the selectivity to product at

30 minutes

4.33 The effect of hydrogen flow rate on the selectivity to product at

60 minutes

4.34 The effect of hydrogen flow rate on the selectivity to product at

90 minutes

A.1 NH3-TPD of HZSM-5

A.2 The pathway reaction of hydroprocessing of tetradecanoic acid

A.3 The pathway reaction of hydroprocessing of dodecanoic acid

A.4 The pathway reaction of hydroprocessing of decanoic acid

A.5 The pathway reaction of hydroprocessing of octanoic acid

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CHAPTER 1 INTRODUCTION

This chapter presents background, objectives, scope and expected outcomes of this work.

1.1 Background

Due to worldwide environmental concern and the increasing fuel demand,

this energy source is being steadily substituted by available renewable sources of liquid

fuels such as biofuels, alcohols and vegetable oil. The transformation of vegetable oil

to biofuel offers environmental benefits since they are renewable, available, low sulfur

and aromatics and bio-degradable. Similar to fossil fuel derived from petroleum,

vegetable oil is possible to be thermochemically converted to biofuels such as

unfinished gasoline, kerosene, and biodiesel (Kimura et al., 2016; Zandonai et al., 2016).

There have been many researches about biodiesel production by either the

transesterification of vegetable oils and animal fats or by the esterification of refined

fatty acid esters. The vegetable oils transesterification with short-chain alcohols is

carried out by acid or basic catalysts while the esterification of free fatty acids (FFA)

present in animal fats with alcohols is carried out over heterogeneous acid catalysts

(Kappally et al., 2015). As a result, the products derived from these syntheses are

glycerol and esters of the renewable fuel or so-called biodiesel. The selection criteria

of feedstock type depends on its domestic availability, cost and quality. Based on the

domestic feedstock yield per harvest areas, palm oil and coconuts have the first and

second highest potential as precursor for biodiesel production, respectively

(Nimmanterdwong et al., 2015). Hence, waste virgin coconut oil with high fatty acid

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content (Oliveira et al., 2010) a possible alternative biofuel feedstock, is available at

no-to-low price and does not have niche applications.

World energy consumed by transportation sector has been substantially

increased higher than industry and household (Yilmaz et al., 2017). The transportation

energy consumption projected for 2020 will be 74% of total petroleum-based energy.

The aviation section, a major transportation subsector, depends on fossil fuels

contributing to atmospheric pollution. Numerous researches have been conducted to

develop sustainable alternatives derived from biomass for aviation (Neuling et al.,

2018).

Biofuel, renewable energy, can replace commercial petroleum-based

products. In recent years, many researchers have focused on development of the

hydrocarbons production from biomass such as clean gasoline, kerosene, and diesel

to reduce environmental problems (Kimura et al., 2013; Zhao et al., 2015). Vegetable

oils or animal fats, as an organic matter, is mostly used as biofuel cropsuch as

sunflower (Rasyid et al., 2015; Zandonai et al,, 2016), coconut (Charusiri et al,, 2006;

Anad et al., 2016), castor (Nasikin et al., 2009), soybean (Sotel-boyas et al., 2008),

canola, cotton (Sotel-boyas et al., 2011), Jatropha curcas (Hanafi et al., 2015), and palm

oil (Sirajudin et al., 2013; Chang et al., 2013). The use of vegetable oils for biofuel

production offers benefits because they are renewable, readily available, low aromatic

and sulfur content and bio-degradable. Moreover, byproducts of esterification and

transesterification processes are glycerol which is precursor for soap manufacturing.

Due to high viscosity and oxygen content and poor atomization and lubricity of various

oils derived from plants and animals can be used as in engine with modification to

meet strict fuel quality. The feedstock choice depends on its availability, and cost.

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Coconut oil extracted from fresh mature kernel of coconut is known as

virgin coconut oil (VCO). Nowadays, (VCO) has gain a lot of public attention in the

scientific research. The extraction process of VCO is obtained by either mechanical or

natural means without applying heat, chemical refining, bleaching or deodorizing to

avoid deteriorating oil quality.

In the production process of virgin coconut oil, abundant waste oils

contains free fatty acid (FFA) similar to the FFA in crude coconut oil are generated. The

low quality waste virgin coconut oil are potential feedstock for bio-oil production.

1.2 Objectives

Due to high FFA content of abundant waste virgin coconut oils, this study

aimed to synthesize ZSM-5 zeolite catalyst for hydrocracking of biofuel production

such as gasoline, kerosene, and diesel.

The objectives are listed as follows:

i. To determine the effect of hydrocracking conditions such as temperature,

pressure, and reaction time on yields of gasoline, biodiesel and kerosene.

ii. To find optimal preparation condition for biofuel production using modified

ZSM-5.

iii. To develop input-output model for predicting yields of gasoline, biodiesel and

kerosene in catalytic hydro-treating.

1.3 Scope

Waste virgin coconut oils, potential feedstock, are converted to biofuels

such as gasoline, biodiesel and kerosene by modified ZSM-5 catalysts. Generally, the

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rate of cracking and the final product depend on the temperature, pressure, and

presence of catalysts. Activity of catalysts was investigated in hydrocracking of waste

virgin coconut oil in a high-pressure reactor system using hydrogen gas.

The reaction temperature for hydrocracking experiments were in a range

of 350 to 400°C, initial hydrogen pressure between 20 and 40 bar, and reaction period

varied between 1 and 3 h. The production of biofuel under the different conditions

was then analyzed by distillation. The yield, conversion and selectivity of each biofuel

type produced were estimated and predicted by an input-output model.

1.4 Expected output

1. Value-added conversion of waste virgin coconut oil is achieved towards

zero waste generation.

2. An input-output model is developed to predict yields of biofuels at

various temperature, initial hydrogen pressure, and reaction period.

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CHAPTER 2

LITERATURE REVIEW

This chapter describes theory and background related to indirect and direct

hydrocracking process and the treatment of zeolite catalyst involved. The effect of

parameters such as the reaction temperature, initial hydrogen pressure, and reaction

time on products yield.

2.1 Vegetable oil

A vegetable oil containing triglyceride is extracted from fruits or seeds of

plants such as olive, soybean, coconut, corn, peanuts, cotton seed and palm nuts. Like

other plants, oil crops use sunlight and photosynthesis for their growth and eliminate

carbon dioxide (CO2) from the Earth’s atmosphere. During a combustion of engine,

carbon dioxide is exhausted. Then the oil crops consume carbon dioxide emitted in

the atmosphere resulting in reducing amount of greenhouse gas emission. Nowadays,

there is a limit availability of fossil fuel resources, i.e., natural gas, petroleum and coal.

Therefore, fossil fuels cannot replenish rapidly to satisfy the growing energy demand

resulting in development of renewable energy derived from natural sources such as

wind, solar, hydro, tide and biomass which can be used as fossil fuel substitute.

Especially, the use of vegetable oils as alternative sources is increasingly interesting for

many reasons, such as environmentally friendly, sustainable sources, and low

production cost. Hydrocarbons produced by vegetable oils such as coconut oil (Kimura

et al., 2013), sunflower oil (Zhao et al., 2015), soybean oil (Ishihara et al., 2014;

Zandonai et al., 2016), jatropha oil (Anand et al., 2016), palm oil (Siregar et al., 2005,

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Budianto et al., 2014), Calophyllum inophyllum oil (Hafshan et al., 2017), Sunan

candlenut oil (Muhammad et al., 2017) and rapeseed oil (Simacek et al., 2009).

The various types of renewable energy sources mostly depend on regional

climate conditions. For example, research using canola oil and coconut oil have been

served as industrial raw materials in biofuel conversion processes in Canada (Adjaye &

Bakhshi, 1995; Idem et al., 1997) and in Philippines (Arida et al., 1986), respectively.

Palm oil has been widely used as the renewable energy source in Malaysia, where is

the largest producer of palm oil in the world (Salam et al., 1996; Mahmud, 1998, Bhatia

et al., 1998, Twaiq et al., 1999). Generally, most vegetable oils contain fatty acids

whose carbon numbers ranging from C14 to C20 while the fatty acid composition of

coconut oil ranges from C6 to C20 as presented in Table 2.1.

Table 2.1

The composition of fatty acid in various types of vegetable oils (Mueller, 2013)

Type of oil Composition (%w/w)

caproic acid

caprylic acid

capric acid

lauric acid

myristic acid

palmitic acid

stearic acid

arachidic acid

Coconut 0.04±0.2 7±2.0 8±2.0 48±4 16±3.0 9.2±1.5 2±1.0 0.25±0.2

Corn 4±0.8 7±1.2 0.6±0.4 10±2 3.5±1.5

Cottonseed 0.4±0.2 20±2.5 2±0.6

Palm kernel 4±1 5±2 41±5 16±2 8±1.0 2±0.8

Olive 0.65±0.

2 11.5±4 2±0.5 0.22±0.12

Soybean 0.5±0.2 9±2 4±1.5

Sunflower 3.7±1.5 2±0.8 2.3±1.2

Peanut 7.5±1.5 4.5±1.8 3±1.2

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The chemical structure of triglyceride vegetable oil extracted from a variety

of plants is shown in Figure 2.1. Fatty acid chains vary in lengths, measured as the

number of C-molecules in the chain, and saturation. Saturations are no “missing” H-

molecules in the fatty acid chain.

Figure 2.1 Chemical structure of vegetable oil (Dutton, 2018)

Several researchers have been conducted the hydrocracking process that

can crack vegetable oils into biofuel products. Marlinda et al. (2016) obtained the

highest yield of gas oil derived from Cerbera manghas oil about 46.45% by using Co-

Ni/HZSM-5 catalyst under hydrogen initial pressure of 15 bar in a batch reactor. The

conversion of Calophyllum inophyllum oil into liquid biofuel has reported by Rasyid

et al. (2015). The hydrocracking process was operated at 350°C and 30 bar with non-

sulfide CoMo catalyst. The yields of biofuel were 25.63 wt% gasoline, 17.31 wt%

kerosene, and 38.59 wt% diesel with CoMo/γ-Al2O3 catalyst. Moreover, CoMo/ γ-Al2O3

catalyst provides higher conversion than CoMo/SiO2 and CoMo/γ-Al2O3-SiO2. When

comparing a various vegetable oils, i.e., palm oil, soybean oil, and canola oil, the

biofuel production from the palm oil produces more liquid products and light C2-C4

olefins than soybean oil and canola oil (Mustafa et al., 2012).

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2.1.1 Coconut oil

The tropical countries have used coconut from the tree Cocos

nucifera, Family Aracaceae (palm family) for thousands of years (Kappally et al., 2015).

The production of coconuts is mostly in South Asia, such as India, the Philippines,

Thailand and Indonesia. Coconut oil or copra oil, is actually an extracted from the

kernel or meat of mature coconuts of coconut palm (Cocos nucifera) with many

applications. All parts of the coconut tree such as meat, water, husk shell, wood, and

leaves are useful in terms of significant economic value, therefore coconut palm is

commonly known as the "Tree of Life" (Gervajio, 2005).

Figure 2.2 Coconut palm Information Nigeria. (2016). Retrieved from

http://www.informationng.com

Coconut oil usually has the composition of the fatty acids between

twelve carbons and twenty carbons. Lauric acid (12:0) content, about 45–56% of the

coconut oil fatty acid compositions, is the major component; however, a variation of

fatty acid contents in coconut oil depends on the coconut variety as shown in Table

2.1.

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2.1.2 Virgin coconut oil

Generally, clear or colourless virgin coconut oil (VCO) is the purest

form of coconut oil and directly extracted from fresh coconut kernel by either

mechanical or natural means, with or without the use of heat, and no chemical refining,

bleaching or deodorization (Villarino et al., 2007). Due to the powerful antimicrobial

and antiviral properties of virgin coconut oil bearing significant amount of short to

medium-chain fatty acids and natural vitamin E, this drives the global increase of VCO

demand in manufacturing pharmaceutical, natural food and cosmetics products.

Figure 2.3 Virgin coconut oil Roxas Sigma Agriventures, Inc. (2016). Retrieved from

http://www.roxassigmaagri.com

Other types of edible coconut oil is refined, bleached and

deodorised coconut oil (RBD) which is derived from copra. The dried coconut kernel

can be achieved by the processes of sun drying, smoke drying or hot air drying. Refined,

bleached and deodorised coconut oil (RBD) and VCO have the same physical and

chemical characteristics, but have different sensory attributes and prices. Free fatty

acid (FFA) content in VCO and palm oil contain high content of saturated fatty acids

as shown in Table 2.2, so it is possible to be transformed to more valuable

hydrocarbon such as biofuel for vehicle and bio-LPG (Liu et al., 2012).

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Table 2.2

Free fatty acid (FFA) in virgin coconut oil (Dayrit et al., 2011)

Free fatty acid % FFA composition

caproic (C6:0) 0.24-0.56

caprylic (C8:0) 4.15-9.23

capric (C10:0) 4.27-6.08

lauric (C12:0) 46.0-52.6

myristic (C14:0) 16.0-19.7

palmitic (C16:0) 7.65-10.1

stearic (C18:0) 2.73-4.63

oleic (C18:1) 5.93-8.53

linoleic (C18:2) 1.00-2.03

Hydrocracking reaction of coconut oil into gasoline fraction has been

performed using mesoporous Ni/modified natural zeolite catalyst at various

temperatures (Salim et al., 2016). After GC-MS analysis of liquid organic product, it

indicates that the hydrocracking of coconut oil involves disconnection (cracking) of C-

C bonding, hydrogenation, isomerization, cyclization and deoxygenation. A variation of

distribution of yields depends on catalytic reaction with a various of temperatures. At

temperature of 450°C the highest conversion of coconut oil to gasoline fraction (C7-

C12), diesel fraction (C13-C18), and heavy fraction (>C18) were 11.73 wt%, 4.82 wt%,

and 15.07 wt% respectively.

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2.2 Hydrocracking

There are several conversion methods of vegetable oils to biofuels such

as transesterification, thermal cracking, catalytic cracking, and hydrocracking (Zhao et

al., 2015; Rasyid et al., 2015; Zandonai et al., 2016; Charusiri et al., 2006; Anad et al.,

2016). Transesterification of triglycerides containing vegetable oils with an alcohol

(methanol or ethanol) in the presence of catalyst is a decomposition of glycerin-fatty

acid linkages into glycerol and esters of biofuel (Kappally et al., 2015). As a result the

product derived from this synthesis process is biodiesel. Thermal cracking process is

usually used to crack heavy hydrocarbons of vegetable oil into lighter hydrocarbons

as biofuel by thermolysis under high temperature, high pressure without catalyst. If the

product residence time in the reactor is so long that the overcracking of hydrocarbon

conversion products takes place, (Salim et al., 2016; Verma et al., 2015). Therefore, the

development of thermal cracking process for producing middle distillates has been

limited. Similarly, a catalytic cracking method can transform vegetable oil as raw

material into biofuel under high pressure of hydrogen causing formation of coke on

the catalyst and olefinic and aromatic compound in products.

In the 1980’s many researches has attempted to shorten the long chain

hydrocarbons of vegetable oils to produce gasoline, kerosene, and diesel.

Hydrocracking is a process that combines between catalytic cracking and

hydrogenation together to produce more desirable products. The process needs high

temperature (300 - 400˚C), high pressure, and catalytic activity. More energy also needs

to crack vegetable oils into hydrocarbons to produce more desirable products.

However, the properties of products such as oxidation stability increased and cetane

numbers are improved by hydrocracking process (Can et al., 2012). The reduction of

biofuel production cost and the improvement of product yield can be achieved by

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development of good selectivity and long lifetime catalysts. The two functions of

catalyst are acidic function and metallic function. The acidic sites provide for the

cracking and isomerization, while the metallic sites as the metals loaded of the support

provide for the hydrogenation. High acidity tends to cause coke on the surface of

catalyst, which leads to deactivation. A good balance between the two functions has

to be maintained for a suitable hydrocracking catalyst. Moreover, the properties of the

products by hydrocracking process are considerably better more than by the

transesterification (Salwa et al., 2015).

Figure 2.4 The possible reaction pathways (Kim et al., 2014 and Veriansyah et al., 2012)

The possible pathways consist of a series of reactions that take place during

hydroprocessing as illustrated in Figure 2.4. During hydroprocessing, double bonds that

contain in triglycerides, it becomes saturated triglycerides at high temperature

hydrogen. The resulting free fatty acid and propane occur, when the saturated

triglycerides are continuously cracked. The production of straight-chain alkanes can be

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occurred through hydrodeoxygenation, decarbonylation, or decarboxylation. Oxygen

removal in the form of water is achieved by saturation of C=O, followed by breaking

of C-O and C-C bonds during hydrodeoxygenation (Bezergianni et al., 2015), while

carbon dioxide (CO2) and carbon monoxide (CO) are produced during decarboxylation

and decarbonylation, respectively (Mohammad et al., 2013). The quantity of resulting

products can be transformed into isomers, aromatics, light hydrocarbons and cyclo-

compounds that depend on the operating parameters and types of catalysts (Kim et

al., 2014; Mohammad et al., 2013; Veriansyah et al., 2012).

2.2.1 Hydrocracking catalysts

The dual-function catalysts of hydrocracking catalysts containing two

distinctly different kinds of sites were first introduced by Mills et al. (1953) and later

expanded by Weisz et al. (1962) and Sinfeld (1983). These studies showed that both

metallic and acid sites must be present on the catalyst surface to achieve all the

desired hydroprocessing reactions, i.e. hydrogenation, dehydrogenation, hydrocracking

etc. The acidic sites promote isomerization reactions and the cracking reactions of C-C

bonds from high molecular weight hydrocarbons, while the metallic sites promote the

hydrogenation-dehydrogenation reactions. Metallic sites are the important sites since

they can avoid undesirable secondary reactions resulting in favorable hydrocracking

catalyst. Hydrogenation sites located in the proximity of the cracking (acid) sites gives

rapid molecular transfer.

2.3 Zeolite

Zeolites are inorganic porous materials. The unique structure of zeolites

pores allow some molecules to pass through their pores. Zeolite is crystalline alumino-

silicate with fully cross-linked open framework structures which contains atoms of

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silicon (aluminum) one atom and four oxygen atoms (SiO4 and AlO4) shown in Figure

2.4. Thus, zeolites are typically unique framework structures and pore diameter of 3-

13 Aº (Moissette et al., 2017).

Figure 2.5 Structure of zeolite (Marcus, Bonnie et al., 1999)

Zeolites can be classified by their chemical structure. Due to their

interesting properties such as its acidity, specific pore structure and unique shape

selectivity, they are used in various industries applications. One of the important uses

of zeolite is as catalytic crackers in processes such as hydrocracking, aromatization and

isomerization of the petrochemical industry where they are used to break the large

hydrocarbon molecules into gasoline, diesel, and kerosene (Corma, 1995; Garcia et al.,

2002; Flanigen, 1980). The advantages of zeolites are less corrosive, less toxic,

environmentally-friendly and easy modification of their acidity and pore-size by ion-

exchanging (Bin, 2007; Busca, 2007).

2.3.1 The structure of zeolite

The 3D structure of the zeolite is made up of corner sharing

aluminum oxygen tetrahedron (AlO4) and silicon oxygen tetrahedron (SiO4), consisting

of alumino-silicate at connection of the oxygen atoms which is copolymer. A

representative formula of zeolite can be presented as below:

Mn.Al2O3.xSiO2.yH2O

where n is the valence of the cation (M)

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x is the number of moles of SiO2

y is the number of moles of water in the zeolite crystals.

The classification of zeolites based on pore size and number of

tetrahedral in the ring is divided into three major groups. The first group has shape-

selective small pore size, called the 8-membered oxygen ring system. Zeolite A and

ZSM-34 are the examples of zeolites catalyst in this group. The second group is a

medium pore zeolites, known as 10-membered oxygen ring system. The unique crystal

structure like ZSM-5 zeolite are in this group.

The last group of zeolites has dual pore system, since they have

interconnecting channels between 8 – and 12 – membered oxygen ring opening or 8

– and 10 – membered oxygen ring opening. The acidic properties of catalyst in this

types can cause coke formation leading to deactivate rapidly.

(a) small pore zeolites (b) medium pore zeolites (c) large pore

zeolites

Figure 2.6 Various types of zeolites; (a) small pore zeolites, (b) medium pore zeolites,

(c) large pore zeolites (Xiaowen et al., 2006)

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2.3.2 Shape Selectivity

Three different types of the shape selectivity including reagent

selectivity, product selectivity, and transition state selectivity are shown in Figure 2.7.

Figure 2.7 Shape selectivity in zeolite channels (Csicsery et al., 1984)

Reactant shape selectivity occurs when only the certain dimensions

of the reactant molecules can permeate into zeolite pore. The reactant molecule that

has smaller diameter than the pore diameter of zeolite can enter into the pores of

zeolite and access the active sites placed in the zeolite pores. On the other hand, the

large diameter cannot diffuse into the pores of zeolite.

Product shape selectivity avoids oversized product molecules from

diffusion through the pores. However, the disadvantage of product shape selectivity is

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large molecules, which are unable to leave from the pores causing desirable product

conversion to undesired side products, coke formation and catalyst deactivation.

Transition state shape selectivity occurs when its transition state requires more space

than available space in the pores.

2.3.3 ZSM-5

ZSM-5 is a type of zeolite that comes from Zeolite Socony Mobile-

Five, was discovered in the early 60’s. ZSM-5 is constructed on 10-membered ring

building unit and these building units link together with each other to form a chain.

The interconnection of these chains then forms a channel system of the ZSM-5 as

shown in Figure 2.8.

Figure 2.8 Scheme of the channel system in ZSM-5 (Scherzer, 1990)

ZSM-5 is usually used in an acidic form. There are two types of acid

sites, which are Bronsted acid sites and Lewis acid sites. Na+ ions of the zeolites are

required to balance the framework charges by which they can be exchanged for

protons by a direct reaction with an acid giving surface Si-OH and Al-OH hydroxyl groups

and this is identified as Bronsted acid sites. If zeolite is not stable in an acid solution,

the ammonium (4NH ) salt is usually formed. After that heating is applied, a proton is

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dissociating due to the removal of ammonia. The oxygen of the hydroxyl is considered

to be three-coordinate, bridging between Si and Al. When heating is further applied,

water from the Bronsted acid sites is removed, exposing Al ion containing vacant site

of orbital which can accept electron pair, known as Lewis acid sites.

For the catalytic cracking process, the acidity of catalysts is not only

the main role in the conversion of waste virgin coconut oil but other parameters of

the microporous materials, i.e., pore size, pore volume and surface area, also influence

the % conversion and % yield of biofuel produced. The highest activity of HZSM-5 may

be attributed to its pore size which is closer to the size of triglyceride molecule. Twaiq

et al. (1999) reported the catalytic cracking palm oil over HZSM-5 and USY catalysts.

The highest yield of gaseous product over HZSM-5 is achieved.

Figure 2.9 Scheme for generating Bronsted and Lewis acid sites in zeolites (Smart and

Moore, 1992)

Many researchers have synthesized various kinds of catalysts for

catalytic cracking process. Some noble metal catalysts such as Pt, Pd, and Ru have an

excellent catalytic performance, but they are limited due to their availability and high

cost. Additionally, the noble metal catalysts are so sensitive to the catalyst

contamination that it can cause deactivation of the catalysts.

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Selection of hydrocracking catalyst for particular biofuel production

has been studied. The catalytic cracking has been studied with used palm oil as raw

material over composite zeolite (Chang and Tye, 2013). The reaction was operated

under the reaction temperature of 350˚C for an hour in a batch reactor. HZSM-5 zeolite

was selected as a catalyst in the study because of its strong acidity and shape

selectivity. To compare catalysts performance with synthesized HZSM-5 zeolite, the

zeolite catalysts were loaded with three different metals, e.g., Zn, Cu, and Mg. HZSM-

5 gave the highest yield of kerosene, while Zn-HZMS-5 catalyst gave the highest

conversion at 26.74 wt%.

The catalytic cracking of palm oil was conducted using HZSM-5 as

catalyst and the reaction was carried out between temperatures at 350°C and 500°C

for 120 min in a fixed bed reactor (Sirajudin et al., 2013). The yields of biofuels were

28.87%, gasoline, 16.20% kerosene, and 1.20% diesel. Furthermore, the HZSM-5

catalyst show more improvement in cracking palm oil to biodiesel compared to

Pt/HZSM-5 and Pd/HZSM-5 (Budianto et al., 2014). HZSM-5 catalyst impregnated by Pd

and Pt showed more enhancement for both yields of biofuels and the selectivity of

biodiesel than HZSM-5 catalyst. At a temperature of 450°C the Pt/HZSM-5 catalyst gave

the highest selectivity and yield of biodiesel of 94.6% and 67.2%, respectively. At a

temperature of 500°C the Pd/HZSM-5 catalyst gave the highest selectivity and yield of

biodiesel of 93.2% and 65.2%, respectively. At a temperature of 350°C using HZSM-5

catalyst, the highest yield of biogasoline biokerosene were 23.0% and 22.5%,

respectively while the lowest yield was 0.7% at a temperature of 400°C using Pt-HZSM-

5. The use of Pt/HZSM-5 and Pd/HZSM-5 catalysts lowered the biokerosene yield to

10.9% and 11.9%, respectively. Therefore, the Pt/HZSM-5 and Pd/HZSM-5 catalyst are

suitable for palm oil cracking process into biofuel, especially biodiesel.

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Zandonai et al. (2016) studied the production of petroleum by

hydrocracking of crude soybean oil over zeolite. The hydrocracking of soybean oil was

performed over NaZSM5 and HZSM5, which were modified ZSM5 catalyst by ion

exchange with ammonium chloride solution. The reaction was performed at 723 K and

138 kPa under a flow of hydrogen gas. The result showed that the increased acidity of

HZSM-5 improved the hydrocarbon production giving products in the range of gasoline.

After 90 min reaction time, the catalyst HZSM5 gave higher selectivity of hydrocarbon

than NaZSM5.

2.4 Parameter condition

A hydrocracking process of vegetable oils is very complex reaction system,

which is influenced by a variety of process parameters including hydrocracking

temperature, hydrogen pressure, and reaction time. In this section, some important

operating parameters are discussed.

2.4.1 Effect of temperature

Temperature, one of main parameters in hydroprocessing, influences

the biofuel yield, catalyst effectiveness and catalyst life (Scherzer and Gruia, 1996). At

the increase of temperatures, the catalyst activity increases and the catalyst

performance is deactivated faster. The removal of oxygen from the final products is

low at low temperatures, while it is more favorable at higher temperatures. The

increase of temperature is more preferable to lighter hydrocarbon production, while

the decrease of temperatures are more suitable for production of diesel range product.

As increasing temperatures, cracking reaction tends to complete resulting in an increase

of smaller and lighter molecules derived from heavy fraction product, such as

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kerosene, gasoline and gases components. Moreover, the properties of cloud point

and pour point has been improved with increasing temperature (Satyarthi et al., 2013).

In the refineries industrial, the operating over temperature range

between 553K (280°C) and 683K (410°C) are favorable. The reaction rates trend to be

slower under 553K, while the temperature above 683K favors undesirable side reaction

and coke formation on the catalyst leading to the decrease of catalyst activity

(Hobson, 1984; Speight et al., 2000). However, the reaction must be carried out at

above 350°C to eliminate the oxygenated compounds in hydrocarbon biofuel, as an

important step in formation of non-renewable fossil fuels (Muhammad et al., 2017).

Furthermore, the increase of hydrocracking temperature promotes the removal of

heteroatom (S, N and O) and deoxygenation (Bezergianni et al., 2009).

In hydrocracking of Cerbera manghas oil using Co-Ni/HZSM-5 in batch

reactor, the effect of the reaction temperature on yields of biofuel was studied by a

variation of reaction temperatures in the range between 300 and 375°C at reactor

pressure of 15 bar for 2 h (Marlinda et al., 2016). The highest yield of diesel was

obtained 46.45% at temperature of 350°C. As temperature increasing, the conversion

activity of hydrocracking of long chain of hydrocarbon molecules into short chain

hydrocarbon molecules was improved as reported in the study of Kim et al. (2013).

The effect of temperature ranging from 350 to 400°C on liquid yield

was investigated by hydrotreating of rapeseed oil with Pt/Zeolite (Pt/H-Y and Pt/HZSM-

5) and NiMo/Al2O3 catalysts in a batch reactor (Sotelo-boyas et al., 2011). At higher

temperature, the liquid yields tend to decrease, while the gas products (methane,

butane, propane and ethane) are observed. Can et al. (2013) employed the

hydrocracking of jatropha oil into green diesel by Ni-HPW/Al2O3 under various reaction

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temperatures from 300°C to 360°C. The increased temperature to 360°C gave 99.85%

conversion of jatropha oil and 85.52% selectivity of diesel fraction.

Marlinda et al. (2017) conducted the hydrocracking process at various

temperatures of 300-375°C for 2 h under hydrogen initial pressure in batch reactor

equipped with a mechanical stirrer. The yield of diesel was increased when the

temperature increasing from 300 to 350°C while the yield of diesel was reduced from

70.08% at a temperature of 350˚C to 66.42 % at a temperature of 375°C. This decline

may be attained to the occurrence of cracking of C18-C23 hydrocarbons into kerosene

(C10-C13).

The prices of the used cooking oil are cheaper than virgin vegetable

oils at least 2-3 times (Zhang et al., 2003). Bezergianni et al. (2009) studied the

hydrocracking process of used cooking oil to produce biofuel under the reactor

temperatures of 350, 370 and 390°C. As increasing the temperature to 390°C, the

conversion increased from 73% to 82%. At higher temperature, the yield of gasoline

was increased from 2 to 10%. The higher degree of cracking reaction can be achieved

with increasing temperature. As the result the feedstock molecule is converted to

diesel molecules which are further cracked into lighter molecules causing reduction of

the diesel selectivity.

The hydrotreating process of waste cooking oil under various of

reaction temperature was studied by Bezergianni et al. (2010). The process was

operated under five different reactor temperatures of 330, 350, 370, 385 and 398°C.

The results revealed that production of gasoline fraction is more favorable at higher

reactor temperatures, while that of diesel fraction are more suitable at lower reaction

temperatures.

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Table 2.3

Previous studies on the effect of temperature.

Source Catalyst Reactor Feedstock Operating parameters

Bezergianni et al. (2010) NiMo Fixed bed Waste cooking oil

T = 330-398°C

P = 80.2 bar

LSHV = 1 h-1

Sotelo-boyas et al. (2011)

Pt/H-Y

Batch Rapeseed oil

T = 300-400°C

Pt/H-ZSM-5 P = 50-110 bar

Time = 3 h

Can et al. (2013) Ni-HPW/Al2O3 Fixed bed Jatropha oil T = 300-360°C

Marlinda et al. (2016) Co-Ni/HZSM-5 Batch Cerbera manghas oil

T = 300-375°C

P = 15 bar

Time = 2 h

Marlinda et al. (2017) Co-Ni/HZSM-5 Batch Cerbera manghas oil

T = 300-375°C

P = 10-15 bar

Time = 2 h

2.4.2 Effect of hydrogen pressure

The main parameter promoting the hydrotreatment of vegetable oils

as reactants is hydrogen pressure. Operating condition at higher hydrogen pressure can

help the water removal from the catalyst to avoid excessive catalyst deactivation. The

higher hydrogen pressure favours the hydrodeoxygenation of triglycerides, while the

decarboxylation decreases (Satyarthi et al., 2013) as shown in reactions (R 2.1) and (R

2.2), respectively. Moreover, higher hydrogen feed rate favors saturation and

heteroatom removal.

Hydrodeoxygenation reaction:

CnH2n+1COOH + 3H2 Cn+1H2n+4 + 2H2O (R 2.1)

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Decarbonylation reaction:

CnH2n+1COOH CnH2n + H2O + CO (R 2.2)

Decarboxylation reaction:

CnH2n+1COOH CnH2n+2 + CO2 (R 2.3)

Kim et al. (2013) studied the effect of pressure on the liquid product

by hydroprocessed soybean oil. The experiment was operated in a batch reactor using

Ni as catalyst under a fixed operating reaction temperature of 400°C and an initial

hydrogen pressure ranging from 2.5 to 12 MPa. When increasing pressure from 9.2 to

12 MPa, the diesel yield decreased while the jet fuel selectivity increased.

At the increase of pressure, conversion and yield of diesel increase.

However, above the optimum level of operating pressure conversion increases while

diesel yield decreases. Kiatkittipong et al. (2013) conducted the hydroprocessing of

crude palm oil (CPO) using Pd/C catalyst under a variation of the hydrogen pressure

from 20 to 60 bar. The conversion of CPO progessively increased whereas diesel yield

increased to its maximum value at 40 bar and decreased at higher pressure. They

obtained the highest diesel yield of 51% under the operation of 400°C, 40 bar and

reaction time of 3 h.

Similar effects were observed in canola oil over Pt/H-Y zeolite,

Pt/HZSM-5 and NiMo/γ-Al2O3 for hydrocracking of canola oil in a batch reactor (Sotel-

Boyas et al., 2010). The experiments were carried out under three parameters including

temperature (300-400°C), initial hydrogen pressure (5-11 MPa), and hydrocracking time

(1- 6 h). The increasing initial hydrogen pressure from 8 to 10 MPa and a fixed

hydrocracking at 350°C for 3 h, diesel yield is slightly increased. The result showed that

the production of diesel fraction is affected significantly by hydrogen pressure.

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Zaher et al. (2015) studied the production of biofuel via catalytic

hydrocracking of castor oil by CoMo/Al2O3 catalyst. The experiments were carried out

under a variation of temperature between 325 and 475°C and that of hydrogen

pressure between 30 and 70 bar. The highest yield of biofuel product of 87% was

achieved at 325°C and 50 bar. Salwa et al. (2015) studied the hydrocracking of Jojoba

oil for green fuel production using zeolites as catalysts. The experiment was operated

in a high-pressure fixed bed reactor at the temperature ranging from 350 to 425°C at

the pressure of 1.0-5.0 MPa. The conversion of virgin oil to biofuel was achieved only

62.45 wt% at hydrogen pressure of 1.0 MPa. Further increasing hydrogen pressure to

5.0 MPa, conversion increased to 93.36 wt%. At higher hydrogen pressures of 5.0 MPa,

the light fractions are more predominant, therefore the high operating hydrogen

pressure is more suitable for gasoline production rather than diesel production.

To investigate the catalytic cracking of non-edible sunflower oil in a

fixed-bed reactor, ZSM-5 was used as catalyst to produce products in the range of

biojet fuel (Zhao et al., 2015). The operating reaction was operated without addition

of hydrogen at reaction temperatures of 450, 500 and 550°C. The result showed that

the highest reaction temperature at 550°C gave the highest conversion of 30.1%.

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Table 2.4

Previous studies on the effect of initial hydrogen pressure.

Reference Catalyst Reactor Feedstock Operating parameters

Sotelo-boyas et al. (2011)

Pt/H-Y

Batch rapeseed oil

T = 300-440°C

Pt/H-ZSM-5 P = 50-110 bar

Time = 3 h

Kiatkittipong et al. (2013)

Pd/C Batch palm oil T = 350-400°C P = 20-60 bar Time = 0.5-3 h

NiMo/γ-Al2O3

Kim et al. (2013) NiMo-Al2O3 Batch soybean oil T = 300-400°C P = 25-120 bar Time = 2 h

Zaher et al. (2015) CoMo-Al2O3 High pressure micro-reactor

castor oil

T = 325-475°C

P = 30-70 bar

LHSV = 1 - 4 h-1

El Khatib et al. (2015) Zeolite Fixed bed jojoba oil

T = 350-425°C

P = 10-50 bar

LHSV = 1 - 5 h-1

Zhao et al. (2015) ZSM-5 Fixed bed sunflower oil T = 450-550°C

no addition of hydrogen

2.4.3 Effect of reaction time

Increasing the residence time of reaction increases the feedstock

conversion to a certain extent. However, beyond the optimum residence time of the

hydrocracking reaction, the diesel cut products undergoes further cracking resulting in

reduction of the diesel yield.

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Rohmah et al. (2012) studied production of bio-gasoline through

catalytic hydrocracking of waste cooking oil using zeolite as catalyst. The process was

carried out in a 1.0 L autoclave and the conditions were varied temperatures (380-

420°C), initial hydrogen pressure of 8 MPa, reaction time of 60 and 90 min. The highest

yield of bio-gasoline was obtained at temperature of 400°C. The reaction time of 90

min slightly decreased the yield of bio-fuel. The longer reaction time results in

evaporation of light fraction to become gas phase.

Some researchers studied the conversion of waste cooking vegetable

oil in batch micro-reactor using sulfated zirconia as catalyst (Charusiri et al., 2006). The

experiment was operated at temperature range of 400 to 430°C, initial hydrogen

pressure between 10 and 30 bar and reaction time from 30 to 90 min. The production

of light gases and aromatics favors at the reaction time longer than 90 min.

Table 2.5

Previous studies on the effect of reaction time.

Reference Catalyst Reactor Feedstock Operating parameter

Charusiri et al. (2006)

sulfated zirconia

Batch waste cooking oil

T = 400-430°C

P = 10-30 bar

Time = 30-90 min

Rohmah et al. (2012)

Zeolite Batch waste cooking oil

T = 380-420°C

P = 8 MPa

Time = 60-90 min

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CHAPTER III

RESEARCH METHODLOGY

In this chapter, the experimental techniques and analytical methods used are

described. It is divided into three sections as the following: materials; methodology

and characterization techniques such as x-ray diffraction (XRD), scanning electron

microscopy (SEM) and temperature programmed desorption (TPD) of ammonia for

measuring surface acidity of zeolites. The reactor setup for hydrocracking process of

waste virgin coconut oil to biofuel, and the analysis of liquid products by distillation

and gas chromatography-mass spectrometry (GC-MS) technique are presented.

3.1 Chemical and reagents

Waste virgin coconut oil obtained from coconut oil extraction process

without involvement of heat. The zeolite ZSM-5, ammonium (NH4) powders were

purchased from Alfa Aesar. The mole ratio of silica (SiO2)-to-alumina (Al2O3) of the

zeolite was 80:1. Low-grade waste virgin coconut oil (Figure 3.1A) was used for batch

process while high-grade waste virgin coconut oil (Figure 3.1B) was used for continuous

process. The amount of waste virgin coconut oil from Thai Nara Company were

approximately 100-150 litre/day.

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Figure 3.1 Low-grade waste virgin coconut oil (yellow in color) (a) and High-grade

waste virgin coconut oil (clear color) (b)

Fatty acid compositions of low-grade and high-grade waste virgin coconut

oil were analyzed using Gas chromatography (Agilent Technology 7890B, Wilmington,

DE, USA) listed in Table 3.1 and Table 3.2, respectively. Waste virgin coconut oil

contains significant amount of shorter chain fatty acids. Low-grade waste virgin coconut

oil is high in lauric acid of 58 wt% while high-grade waste virgin coconut oil is high in

capric acid of 51 wt%.

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Table 3.1

Analysis data of low-grade waste virgin coconut oil

Fatty acid composition Compound Formula Retention time

(min) wt%

Caprylic acid C8H16O2 8.493 15.65

Capric acid C10H20O2 10.08 11.19

Lauric acid C12H24O2 12.275 58.79

Myristic acid C14H28O2 15.234 14.38

Table 3.2

Analysis data of high-grade waste virgin coconut oil

Fatty acid composition Compound formula Retention time

(min) wt%

Cyclohexanecarboxylic acid C7H12O2 10.60 1.30

Nonenoic acid C9H16O2 8.88 1.18

Capric acid C10H20O2 10.97 51.15

Undecylic acid C11H22O2 16.66 34.02

Dodecenoic acid C12H22O2 13.06 0.30

Lauric acid C12H24O2 21.00 12.05

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3.2 Methodology

The experimental sequence is illustrated in Figure 3.2. Each step is described in details.

Figure 3.2 Experimental procedure

START

Characterization of catalyst

Apparatus setup

Blank Test

Catalytic hydrocracking reaction condition under various Temperature (T), hydrogen pressure (P), reaction time (t)

Product separation by distillation and composition analysis by GC-MS

Preparation of catalyst

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3.2.1 Preparation of HZSM-5 zeolite

Firstly, NH4-ZSM-5 was dried at 100C for 24 hours. Then, the catalyst

NH4-ZSM-5 form zeolite was transformed to the H-form through calcination process at

550C for 5 h. The HZSM-5 catalyst was obtained (Marlinda et al., 2016; Muhammad

et al., 2017) as shown in Figure 3.3.

Figure 3.3 Scheme of HZSM-5 zeolite preparation

3.2.2 Characterization of zeolite

The characteristics of the prepared H-ZSM-5 were analyzed by the

following methods:

3.2.2.1 X-ray powder diffraction

X-ray diffraction technique is employed intensively to obtain

both qualitative and quantitative measurement on the characteristic and the

arrangement of atoms in a crystalline solid matter. X-ray diffraction (Siemens D-500,

Germany) was employed to identify and quantify of crystalline phases in the prepared

HZSM-5. The diffractometer was equipped with Cu K-α radiation 1.5418 Å at 30 mA

and 40 kV. The powder samples were scanned from 5° to 50 ° 2 at 2°/min with a

scanning step of 0.05°/step. Sample for the X-ray analysis was ground gently into a fine

powder and packed approximately 0.3-0.5 g of the sample into an aluminium sample

holder by tightening with light compression.

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3.2.2.2 Scanning electron microscopy

The scanning electron microscopy (JEOL, JSM-7800F, Japan)

was used to analyze the morphology and size distribution of the HZSM-5. Samples

were put on a thin carbon film to avoid charging effect during SEM investigation.

3.2.2.3 Temperature Programmed Desorption

Temperature programmed desorption (TPD) is used techniques

to characterize the acidity of HZSM-5. To measure the acidic and basic strength,

ammonia (NH3) was absorbed on zeolite HZSM-5. The NH3 temperature programmed

desorption (TPD) study was carried out using a heating rate of 10 ºC/min. The pulses

were continued until no more consumption of NH3 was observed.

3.2.2.4 Gas Chromatography-Mass Spectrometry (GC-MS)

The reaction reactant and product would be analyzed by GC-

MS (Gas Chromatography-Mass Spectrometry). It can analyzed both qualitatively and

quantitatively as well. The components comprised would be able to be detected by

means of the instrument with capillary column model number of Agilent Technologies

7890B, HP-Innowax for reactant (waste virgin coconut oil, WCO) and Agilent

Technologies 7890B, HP-5MS for liquid products. The condition of gas chromatography-

mass spectrometry (GC-MS) is presented in Appendix A.2.

3.3 Hydrocracking Process

The hydrocracking of waste virgin coconut oil was performed in a 200 ml

batch reactor equipped with a mechanical stirrer as shown in Figure 3.4. The operative

limits of the reactor were 200 bar and 400°C. The stirrer speed was kept constant at

350 rpm and the temperature control accuracy was ±3°C for all experiments. HZSM-5

catalyst was activated at 400°C for 4 h under a hydrogen pressure of 50 bar. For the

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hydrocracking experiment, approximately 1 g of the HZSM-5 catalyst and 100 ml waste

coconut oil was loaded in the reactor.

Leak test was conducted by loading hydrogen gas up to 70 bar at room

temperature and kept for 30 min to ensure no leak during heating and reaction.

Figure 3.4 Schematic diagram of the batch reactor

Figure 3.5 Batch reactor

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The reaction temperature for hydrocracking experiments were in a range

of 350 to 400°C and initial hydrogen pressure between 20 to 40 bar. The reaction time

was varied between 1 and 3 h to determine the optimal reaction time. The reactor

was then heated up to the final temperature by adjusting the temperature controllers.

When the conditions were reached, the reaction started. Upon the completion of the

reaction, the reactor was cooled to room temperature after finishing reaction by the

cooling unit inside of the reactor Product of hydrocracking was collected, and liquid

product was separated from catalyst by filtration. The reaction products were then

separated by distillation. Distillation technology can be used to separate an oil mixture

with wide boiling ranges into products with narrower boiling ranges. The oil mixture

was heated to vaporize the lighter components (Al-Sabawi et al., 2012). The

performance of catalysts was evaluated in terms of conversion, the yield of production

biofuel, and liquid product fraction as a follows:

𝐶𝑜𝑛𝑣𝑒𝑟𝑠𝑖𝑜𝑛 (%) = initial feedstock (g) −residue (>340˚C)after cracking

initial feedstock (g)x 100% (3.1)

𝑌𝑖𝑒𝑙𝑑(𝑤𝑡%) = weight of fractional distillation of liquid products (g)

initial feed stock (g) 𝑥 100% (3.2)

𝑆𝑒𝑙𝑒𝑐𝑡𝑖𝑣𝑖𝑡𝑦(𝑤𝑡%) = weight of target product (g)

weight of liquid product (g) 𝑥 100% (3.3)

Where initial feedstock and residue (>340C) after cracking are represented by the

wt% of the feed and product, respectively.

𝐿𝑖𝑞𝑢𝑖𝑑 𝑝𝑟𝑜𝑑𝑢𝑐𝑡 𝑓𝑟𝑎𝑐𝑡𝑖𝑜𝑛 (𝑣𝑜𝑙%) = volume of distillation fraction

total volume of distillate obtainedx 100% (3.4)

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Figure 3.6 Distillation

The yields of product were estimated from the distillation of the total

liquid product. The composition of hydrocracking liquid product was classified

according to its boiling range such as gasoline (40°C-160°C), kerosene (160°C-270°C),

and diesel (270°C-360°C). Moreover, long chain hydrocarbon molecule with boiling

point > 360°C the unconverted waste coconut oil that cannot be produced liquid

biofuels.

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CHAPTER IV

RESULT AND DISCUSSION

Results of characterization of the prepared catalyst zeolite using x-ray diffraction,

scanning electron microscopy, and temperature programmed desorption technique

were reported and discussed. The effect of operating parameters, i.e., operating

temperature, operating hydrogen pressure and reaction time, on conversion of waste

virgin coconut oil and yields of liquid biofuels was investigated to determine optimal

operating condition for biofuel production.

4.1 Characterization Analyses

4.1.1 X-ray Powder Diffraction

X-ray diffraction that used to identify multiphases pattern of HZSM-

5 is illustrated in Figure 4.1. The XRD peaks of HZSM-5 showed at the 2θ of 7-9˚ and

23-25˚. The XRD peak position and intensity of the prepared ZSM-5 catalyst are

consistent with the previously reported pattern (Zhao et al., 2015) that amorphous

impurities were not noticeably observed in the material.

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Figure 4.1 XRD patterns of HZSM-5

4.1.2 Scanning electron microscopy (SEM)

After hitting the sample with a focused beam of high-energy electron,

a detector of a scanning electron microscopy collects emitted electrons and photons,

and thus the image is obtained. The SEM images of catalysts were taken at 20000X

and 50000X magnification to observe their surface morphology in Figure 4.2 and 4.3.

The SEM pictures of H-ZSM-5 and ZSM-5 were comparable and they have shapes close

to cubic crystals.

Figure 4.2 SEM images of HZSM-5 (a) X50,000 (b) X20,000 magnificent

a b

100 nm 1 µm

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Figure 4.3 SEM images of ZSM-5 (c) X50,000 (d) X20,000 magnificent

Moreover, EDX spectrum analysis shows that the HZSM-5 structure

contained Si and Al in approximately 97.80: 2.20. (Si/Al ratio is 44.45).

Figure 4.4 EDAX Spectrum

Element Atomic %

Al 2.2

Si 97.8

Total 100

c d

100 nm 1 µm

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4.1.3 Temperature Programmed Desorption (TPD)

The NH3 desorption peaks of HZSM-5 were noticed the ranges of

temperature at 100-300 ºC (T1), 300-500 ºC (T2), 500-700 ºC (T3). The peak I may be

attributed to desorption of NH3 from weak acid sites, whereas peak II and peak III were

observed corresponding to medium and strong acid sites as summarized in Table 4.1

and the detail of TPD-NH3 is presented in Appendix A.4.

Table 4.1

Results of TPD-NH3 analysis over HZSM-5 zeolite

No. Peak type

End time

Time width

Peak position(sec)

Area(count) mmol mmol/g

1 TPx 1227 2323 1097 687,594 0.021 0.364

2 TPx 2324 3710 1387 590,231 0.018 0.312

3 TPx 3711 4807 1097 147,330 0.004 0.078

4.2 Effect of operating parameters on hydrocracking of waste virgin coconut oil

4.2.1 Effect of initial hydrogen pressure

The operating condition was evaluated at three different initial

hydrogen pressure, i.e. 20, 30, and 40 bar are shown in Table 4.2. The remaining

operating conditions were at 400˚C for 1 h over 1 g of HZSM-5.

The hydrocracking process of waste virgin coconut oil using HZSM-5

catalyst as increasing the pressure of 20 to 40 bar at a constant reaction temperature

(400°C) and reaction time (1 h), the liquid product conversion continually increased.

From Table 4.2, the highest the liquid biofuel conversion (Xl) attained was of 66.54

wt% with a hydrogen pressure of 40 bar. At initial hydrogen pressure of 20 bar, only

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63.90 wt% from the waste virgin coconut oil was transformed to liquid biofuel. Upon

increasing the pressure to 30 bar, the liquid product fractions increased to be 64.25

wt% showed in Table 4.2. The liquid product conversion (Xl) was slightly increased

with an increase in initial hydrogen pressure. It probably due to enhanced hydrogen

mass transfer on the catalyst surface, resulting in maximized use of hydrogen for

deoxygenation reactions (Srifa et al., 2015).

Table 4.2

The effect of initial hydrogen pressure on conversion (Xl), yield, and selectivity of liquid

produce fraction for waste virgin coconut oil.

Sample Yield (wt%) Selectivity (wt%) Xl

(wt%) gasoline kerosene diesel residue gasoline kerosene diesel residue

A-1 1.36 19.04 43.50 20.40 1.61 22.59 51.60 24.20 63.90

A-2 1.70 19.75 42.81 19.60 2.02 23.55 51.05 23.37 64.25

A-3 2.72 21.86 41.96 17.40 3.24 26.05 49.99 20.73 66.54

*A-1: T=400 °C, P=20 bar, t=1 h A-2: T=400 °C, P=30 bar, t=1 h A-3: T=400 °C, P=40 bar, t=1 h

When increasing in initial hydrogen pressure, the diesel yield slightly

decreased. The resulted showed the decrease in diesel yield from 43.50 wt% to 41.96

wt% as the temperature increased from 350 °C to 400 °C at a constant reaction

temperature and reaction time. However, the kerosene and gasoline yield slightly

increased with an initial hydrogen pressure. The kerosene and gasoline yield was

increased from 19.04 to 21.86 wt% and 1.36 to 2.72 wt%, respectively. The light

fractions are more predominant at initial hydrogen pressure of 40 bar, indicating that

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this technology is more suitable for kerosene production at relatively higher pressures

rather than diesel production.

The liquid produce fraction including gasoline, kerosene, and diesel

are represented in Figure 4.5. The result found that initial hydrogen pressure had

negligible effect to the overall activity in liquid produce fraction.

Figure 4.5 Effect of initial hydrogen pressure on liquid product fractions (wt%) in the

catalytic hydrocracking of waste virgin coconut oil (Conditions: Catalyst = 1 g of H-ZSM-

5, reaction temperature = 400 ˚C and time = 1 h)

By suggesting that increasing an initial hydrogen pressure from 20 to

40 bar shored insignificant effect towards the liquid product fraction. Due to when the

reaction was operated at high pressure, decarboxylation and decarbonylation as

endothermic reactions are less favoured. The hydrodeoxygenation reaction is favoured,

1.36

1.7

2.72

19.04

19.75

21.86

43.5

42.81

41.96

0 10 20 30 40 50

20 bar

30 bar

40 bar

Liquid product fraction (wt%)

Init

ial

hydro

gen

pre

ssure

(bar

)

diesel kerosene gasoline

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then result in more water forming and less liquid biofuel product because of the

deactivation of the catalyst (Kim et al., 2013).

4.2.2 Effect of reaction temperature

Reaction temperature has been the most important parameter

affecting catalyst performance. The influence of this factor on the yield and quantity

of the hydrocracked products derived from waste virgin coconut oil over HZSM-5

zeolite was studied. Three different reaction temperatures were varied i.e. 350°C,

375˚C, and 400°C while other operating conditions such as initial hydrogen pressure

and reaction period were kept constant at 40 bar for 1 h over 1 g of HZSM-5 in a

powder form. Table 4.3 shows the influence of temperature on the catalytic

hydrocracking waste virgin coconut oil.

The conversion of each reaction temperature is considered by Eq.

(3.1). Waste virgin coconut oil conversion to liquid product was found to be very much

dependent on temperature. Waste virgin coconut oil conversion decreased with

increasing temperature. When increase reaction temperature, the conversion of liquid

biofuel (Xl) decreases from 69.55 to 66.54 wt% when increase temperature from 350˚C

to 400 ˚C at a constant initial hydrogen pressure and reaction time is presented in

Table 4.3. This is because the hydrocarbons formed, cracks to gas product fraction

there by dramatically reducing the liquid product fraction.

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Table 4.3

The effect of temperature on conversion (Xl), yield, and selectivity of liquid produce

fraction for waste virgin coconut oil.

Sample Yield (wt%) Selectivity (wt%) Xl

(wt%) gasoline kerosene diesel residue gasoline kerosene diesel residue

B-1 0.35 10.58 58.62 11.80 0.43 13.00 72.06 14.51 69.55

B-2 0.57 14.11 52.45 15.60 0.69 17.05 63.40 18.86 67.13

A-3 2.72 21.86 41.96 17.40 3.24 26.05 49.99 20.73 66.54

*B-1: T=350 °C, P=40 bar, t=1 h B-2: T=375 °C, P=40 bar, t=1 h A-3: T=400 °C, P=40 bar, t=1 h

Figure 4.6 Effect of temperature on liquid product fractions (wt%) in the catalytic

hydrocracking of waste virgin coconut oil (Conditions: Catalyst = 1 g of H-ZSM-5, Initial

hydrogen pressure = 40 bar and reaction period = 1 h)

0.35

0.57

2.72

10.58

14.11

21.86

58.62

52.45

41.96

0 10 20 30 40 50 60 70

350°C

375°C

400°C

Liquid product fraction (wt%)

Tem

per

ature

(°C

)

diesel

kerosene

gasoline

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With an increasing in temperature, the diesel yield decreased from

58.62 wt% at 350 °C to 41.96 wt% at 400 °C at a constant pressure of 40 bar and the

reaction time of 1 h. Besides, diesel fraction is not favoured with temperature, while

gasoline and kerosene fractions are clearly favoured. This is expected as increasing

temperature causes more intensive cracking thus not only heavier molecules but also

some diesel molecules are further cracked into lighter molecules, there by

dramatically reducing the diesel product. Therefore at higher temperature the

hydrocracking promote gasoline and kerosene rather than diesel production.

The kerosene yield and gasoline yield increased from 10.58 to 21.86

wt% and 0.35 to 2.72 wt%, respectively as the temperature increases from 350°C to

400°C. It is consistent to the studies of that the most suitable temperature for gasoline

and kerosene production was higher than 350°C (Budianto et al., 2014; Sotelo-boyas

et al., 2008). Therefore, the reaction temperature of 350˚C is the most suitable

temperature for diesel production. Moreover, the best gasoline and kerosene fraction

of the desired liquid product can be achieved at 400˚C. On the other hand, the data

confirm the unsatisfactory results obtained for hydrocracking in case of minimizing the

reaction temperature to 350˚C.

4.2.3 Effect of reaction time

Reaction time studied in the range of 1 to 3 h. The influence of

reaction time on liquid produce fraction, under constant experimental conditions, can

be deduced from the results listed in Table 4.4. Diesel fraction is not favoured with

the time of reaction, while the increasing of reaction time is more suitable for the other

two fractions include gasoline and kerosene.

At reaction time of 60 minutes, 66.54wt% from the waste virgin

coconut oil was transformed to liquid biofuel. Upon decreasing the reaction time to

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120 minutes and 180 minutes, the liquid produce fractions was 65.64 wt% and 65.94

wt%, respectively. Increasing the time of reaction reduce the liquid product conversion

(Xl) was reduced to a certain extent as the reaction proceeds beyond the optimum

time of reaction, the diesel cut products undergoes further cracking not only to lighter

produce fraction but also gas produce fraction. Consequently, reduction of the diesel

produce fraction was observed. For waste virgin coconut oil using HZSM-5 the optimum

reaction time of produce kerosene and gasoline was found to be 180 minutes which

there is decrease in diesel produce fraction.

Table 4.4

The effect of reaction time on conversion (Xl), yield, and selectivity of liquid produce

fraction for waste virgin coconut oil.

Sample Yield (wt%) Selectivity (wt%) Xl

(wt%) gasoline kerosene diesel residue gasoline kerosene diesel residue

A-3 2.72 21.86 41.96 17.40 3.24 26.05 49.99 20.73 66.54

C-2 3.06 19.39 43.20 18.40 3.63 23.08 51.40 21.89 65.64

C-3 6.79 31.38 27.77 20.40 7.86 36.35 32.16 23.63 65.94

*A-3: T=400°C, P=40 bar, t=1 h C-2: T=400°C, P=40 bar, t=2 h C-3: T=400°C, P=40 bar, t=3 h

As it is evident from Figure 4.7, the light fractions are more

predominant at reaction time of 180minutes, indicating that long time of reaction is

more suitable for gasoline and kerosene fraction than diesel produce fraction until

overcracking.

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Figure 4.7 Effect of reaction time on liquid product fractions (wt%) in the catalytic

hydrocracking of waste virgin coconut oil (Conditions: Catalyst = 1 g of H-ZSM-5,

Pressure = 40 bar and temperature = 400˚C)

As increasing in the reaction time, the diesel yield dramatically

decreased. The diesel yield decreased from 41.96 wt% at 1 h to 27.77 wt% at 3 h at a

constant reaction temperature and initial hydrogen pressure. However, the kerosene

and gasoline yield increased with the reaction time. The kerosene and gasoline yield

was increased from 21.86 to 31.38 wt% and 2.72 to 6.79 wt%, respectively.

Therefore, the reaction time of 120 minutes is the most suitable

temperature for diesel production. Moreover, it could be regarded as the most suitable

temperature for the light fraction product, particularly kerosene, can be realized the

reaction time of 180 minutes. For the longer time of reaction, the liquid biofuel

undergoes further cracking to the lighter produce fraction and reduces the diesel

produce fraction.

2.72

3.06

6.79

21.86

19.39

31.38

41.96

43.2

27.77

0 20 40 60 80

60 min

120 min

180 min

Liquid product fraction (wt%)

Rea

ctio

n t

ime

(min

)diesel

kerosene

gasoline

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4.3 Data analysis from the input-output model

A quantitative predictive linear model based on can be determined by

calculating input-output coefficients of values of input (reaction temperature, initial

hydrogen pressure, and reaction period) and output (yields of gasoline, kerosene and

diesel). The set of experimental data of hydrocracking of waste virgin coconut oil for

producing liquid biofuel was modeled to estimate input-output coefficients as follows:

The input-output model was proposed as Z = + P + T +t (4.1)

Where Z = 7x1 vector of liquid biofuel yields {YX/S} under all seven conditions,

P = pressure, {20, 30, 40} bar,

T = temperature, {350, 375, 400} ºC,

t = reaction time, {1, 2, 3} h.

It can be written in matrix form as follows:

Z = AB or B = A-1Z

Where A = 74 matrix of the total experimental conditions,

B = 41 vector of model coefficients, [ ]T.

𝑍 = 𝑌𝑔𝑎𝑠𝑜𝑙𝑖𝑛𝑒 = 1 + 1

𝑃 + 1

𝑇 + 1𝑡 (4.2)

𝑍 = 𝑌𝑘𝑒𝑟𝑜𝑠𝑒𝑛𝑒 = 2 + 2𝑃 +

2𝑇 + 2𝑡 (4.3)

𝑍 = 𝑌𝑑𝑖𝑒𝑠𝑒𝑙 = 3 + 3

𝑃 + 3

𝑇 + 3𝑡 (4.4)

The model coefficients were determined by solving a linear matrix

equation with Matlab (Mathworks, MA, USA) as shown in Table 4.5

.

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Table 4.5

The calculated correlation coefficients

α β γ δ

α1 -16.216 β1 0.0298 γ1 0.0371 δ1 2.146 α2 -58.542 β2 0.0044 γ2 0.1822 δ2 4.82 α3 163.229 β3 0.08 γ3 -0.287 δ3 -7.0143

The proposed input-output models were as follows:

Ygasoline = -16.2160 + 0.0298P + 0.0371T + 2.1460t (4.5)

Ykerosene = -58.5420 + 0.0044P + 0.1822T + 4.8200t (4.6)

Ydiesel = 163.2290 + 0.0800P - 0.2870T– 7.0143t (4.7)

Eqs. (4.5)-(4.7) were plotted as shown in Figures 4.8-4.10.

A positive value of represents favorable effect on Ydiesel while a negative

value of represents unfavorable effect on Ykerosene and Ygasoline. The increase of

reaction temperature and reaction time had insignificantly adverse effect on Ydiesel as

shown in corresponding Figures 4.8 and 4.10. Moreover, the increase of reaction time

and temperature had positive effect on Ygasoline and Ykerosene as shown in Figures 4.8 and

4.10. The increase of initial hydrogen pressure had no significant effect on Ykerosene,

Ygasoline, and Ydiesel.

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Figure 4.8 The input-output correlation of the effect of initial hydrogen pressure (P)

Figure 4.9 The input-output correlation of the effect of reaction temperature (T).

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Figure 4.10 The input-output correlation of the effect of reaction time (t).

4.4 Accuracy of models used in liquid biofuel yield prediction

The coefficient of determination that gave a good fit as estimated R2 values

of yield prediction models of gasoline, kerosene, and diesel was 0.9227, 0.8605, and

0.9133, respectively as shown in Figures 4.11-4.13. This shows better fit between

modeled and observed data of Ygasoline and Ydiesel than that of Ykerosene.

Figure 4.11 Correlation between actual and predicted yield for gasoline

y = 0.9231x + 0.1759

R² = 0.9227

0.0

1.0

2.0

3.0

4.0

5.0

6.0

7.0

0.0 2.0 4.0 6.0 8.0

Pre

dic

ted

Yie

ld

Actual Yield

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Figure 4.12 Correlation between actual and predicted yield for kerosene

Figure 4.13 Correlation between actual and predicted yield for diesel

4.5 Data analysis – Pearson’s correlation coefficient

Pearson’s correlation coefficient is a statistical measure of association

strength between two variables. Pearson’s correlation ranges between +1 and -1 where

+1 shows a perfect relationship, -1 shows adverse relationship and 0 indicates no

associaton between two variables. An r value indicates strength in relationship

y = 0.8601x + 2.7051

R² = 0.8605

0.0

5.0

10.0

15.0

20.0

25.0

30.0

35.0

0.0 10.0 20.0 30.0 40.0

Pre

dic

ted Y

ield

Actual Yield

y = 0.913x + 3.8651

R² = 0.9133

0.0

10.0

20.0

30.0

40.0

50.0

60.0

70.0

0.0 20.0 40.0 60.0 80.0

Pre

dic

ted Y

ield

Actual Yield

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between variables as follows: 0 r 0.29, weak; 0.30 r 0.39, moderate; 0.40

r 0.69, strong; and r 0.70, very strong.

For the yield of data, SPSS (version 16, chicago, IL, U.S.) produces the following

correlation output:

Table 4.6

Pearson’s correlation coefficients of yields of liquid biofuel with reaction temperature

(T), initial hydrogen pressure (P), and reaction time (t).

*Significant level or p-value of 0.05

**Significant level or p-value of 0.01

The yield of diesel (Ydiesel) and that of kerosene (Ykerosene) have no

relationship with initial hydrogen pressure (P) indicating P dependence is negligible as

shown in Table 4.6. Moreover, the Ygasoline has a weak positive relationship with P

indicating P dependence of the Ygasoline. Hydrogen pressure is necessary to avoid

deactivation of the catalyst (Donnis et al., 2009; Maki-Arvela et al., 2007). Higher

pressure would enhance the absorbed hydrogen on the surface active sites promoting

hydrodeoxygenation and it produces more water, which may deactivate the catalyst.

Pearson's correlation T P T

Ygasoline Correlation coefficient (r) 0.561 0.258 0.921**

Sig. (2-tailed) 0.190 0.576 0.003

Ykerosene Correlation coefficient (r) 0.749 0.016 0.773*

Sig. (2-tailed) 0.053 0.972 0.042

Ydiesel Correlation coefficient (r) -0.809 0.070 -0.755

Sig. (2-tailed) 0.028 0.882 0.050

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When increasing the initial hydrogen pressure, the improvement of Ygasoline was slightly

more noticeable than that of Ykerosene and Ydiesel. It was consisitent with the study of

Sotelo-boyas et al. (2011) that the Ydiesel is not affected significantly by the pressure.

The Pearson’s correlation coefficients in Table 4.6 shows very strong

negative relationship of the Ydiesel with reaction temperature (T) and time (t) with

corresponding r values of -0.809 and -0.755. On the other hand, the Ykerosene shows very

strong positive relationship with T and t with corresponding r values of 0.749 and 0.773.

The Ygasoline shows very strong positive relationship with t with r value of 0.921 while

this shows strong positive relationship with T with r value of and 0.561. It indicated

that the temperature mainly affected the thermal cracking of long chain hydrocarbon

into light products, and further cracking resulting in a light hydrocarbon gaseous

product with increasing the reaction time. At higher temperature and longer

hydrocracking reaction time, hydrodeoxygenation was favored while the yield of liquid

products was directly affected (Budianto et al., 2014). As shown in Table 4.6, the Ydiesel

was dramatically decreased with increase of temperature, probably due to the

continued cracking reaction of the long chain hydrocarbons to light products such as

kerosene and gasoline. At temperatures above 350C, the capacity of cracking of n-

paraffins and iso-paraffins in the boiling range of diesel was enhanced; which in turn,

the yield of light product fractions as gasoline and kerosene was increased.

4.6 The Reaction Product Distribution

4.6.1 The number of carbon atom

The product samples were collected and analyzed by gas

chromatography (GC-MS). The composition of hydrocracking liquid product was

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classified according to the number of carbon atom such as gasoline (< C8), kerosene

(C9-C12), diesel (C13-C18), and heavy fraction (> C18). The product distribution of C7-C26

hydrocarbons under the various reaction conditions over HZSM-5 catalysts presents as

Figures 4.14 -4.1 6 . Increasing hydrogen pressure increased water removal from the

catalyst to avoid excessive catalyst deactivation. The initial hydrogen pressure as

studied in the range of 20 to 40 bar. The highest distribution of hydrocarbons was in

the range of C11.

Figure 4.14 The effect of initial hydrogen pressure on the distribution of carbon atom

number of liquid products yielded from hydrocracking process over HZSM-5

The increase of temperature was more preferable to lighter

hydrocarbon production, while the decrease of temperatures was more suitable for

production of diesel range product (C13-C18). At the lowest reaction temperature of

350°C, the main product was in the range of C13 as shown in Figure 4.15. Higher

temperature leads to more complete cracking reaction resulting in the increase of

smaller and lighter molecules derived from heavy fraction products, such as kerosene

and gasoline. The elevated reaction temperature improves the catalyst activity;

0

5

10

15

20

25

30

35

40

C7 C8 C9 C10 C11 C12 C13 C14 C15 C16 C17 C18 C19 C20 C21 C22 C23 C24 C25 C26

Sel

ecti

vit

y (

%)

The number of carbon atom

20 bar

30 bar

40 bar

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however, the catalyst performance tends to be deactivated faster (Gutierrez et al.,

2012).

Longer time of reaction brings more conversion of waste virgin

coconut oil to the heavy cracked fraction which was further cracked to the lighter

product fraction. At the reaction time of 120 minutes, the distribution of hydrocarbons

were in the range of C7 (gasoline) and C13-C18 (diesel). When the reaction time was

increased to 180 minutes, the highest distribution of hydrocarbons were in the range

of C9-C11 defined as kerosene range as shown in Figure 4.16.

Figure 4.15 The effect of reaction temperature on the distribution of carbon atom

number of liquid products yielded from hydrocracking process over HZSM-5

0

5

10

15

20

25

30

35

40

45

C7 C8 C9 C10 C11 C12 C13 C14 C15 C16 C17 C18 C19 C20 C21 C22 C23 C24 C25 C26

Sel

ecti

vit

y (

%)

The number of carbon atom

350 C

375 C

400 C

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Figure 4.16 The effect of reaction time on the distribution of carbon atom number of

liquid products yielded from hydrocracking process over HZSM-5

4.6.2 Selectivity of kerosene range hydrocarbon

The product distribution of kerosene range over the HZSM-5 catalyst

was shown in Figures 4.19-4.20 and the number of hydrocarbon C9 - C12 are the main

component in jet fuel. There are many types of compounds in kerosene fraction,

including alkanes, alkenes, and aromatics. The product selectivity in kerosenerange

hydrocarbons containing a C = C double bond known as alkenes which were the major

kerosene fraction under the various conditions.

0

5

10

15

20

25

30

35

40

C7 C8 C9 C10 C11 C12 C13 C14 C15 C16 C17 C18 C19 C20 C21 C22 C23 C24 C25 C26

Sel

ecti

vit

y (

%)

The number of carbon atom

60 minutes

120 minutes

180 minutes

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Figure 4.17 The effect of reaction temperature on the selectivity for kerosene fraction

towards formation of aromatic, alkane, and alkene

Figure 4.18 The effect of initial hydrogen pressure on the selectivity for kerosene

fraction towards formation of aromatic, alkane, and alkene

aromatic

alkane

alkene

0

20

40

60

80

100

350 375 400

Sel

ecti

vit

y o

f ker

ose

ne

ran

ge

hyd

roca

rbo

ns

(%)

Reaction temperature (°C)

aromatic

alkane

alkene

0

20

40

60

80

100

20 30 40

Sel

ecti

vit

y o

f ker

ose

ne

range

hydro

carb

ons

(%)

Initial hydrogen pressure (bar)

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Figure 4.19 The effect of reaction time on the selectivity for kerosene fraction

towards formation of aromatic, alkane, and alkene

4.7 Degree of deoxygenation (DOD) and degree of cracking (DOC)

4.7 .1 Effect of reaction parameters on the degree of deoxygenation

(DOD) and degree of cracking (DOC) in the batch reactor

To analyze the degree of deoxygenation (DOD) of organic acids in the

oil is calculated using Eq. (4.8) correlating the organic oxygenated compounds

produced (Ox). For evaluating the cracking extent of reaction, the degree of cracking

(DOC), Eq. (4.9), was used, which is the relation of the amount of carboxylic acids in

products and in feed. Eqs. (4.8) and (4.9) are expressed as follows:

𝐷𝑒𝑔𝑟𝑒𝑒 𝑜𝑓 𝑑𝑒𝑜𝑥𝑦𝑔𝑒𝑛𝑎𝑡𝑖𝑜𝑛 = (1 −𝑂𝑥𝑦𝑔𝑒𝑛𝑎𝑡𝑒𝑑𝑝𝑟𝑜𝑑𝑢𝑐𝑡

𝑂𝑥𝑦𝑔𝑒𝑛𝑎𝑡𝑒𝑑𝑓𝑒𝑒𝑑) ∗ 100 (4.8)

𝐷𝑒𝑔𝑟𝑒𝑒 𝑜𝑓 𝑐𝑟𝑎𝑐𝑘𝑖𝑛𝑔 = (1 −𝑐𝑎𝑟𝑏𝑜𝑥𝑦𝑙𝑖𝑐 𝑎𝑐𝑖𝑑𝑝𝑟𝑜𝑑𝑢𝑐𝑡

𝑐𝑎𝑟𝑏𝑜𝑥𝑦𝑙𝑖𝑐 𝑎𝑐𝑖𝑑𝑓𝑒𝑒𝑑) ∗ 100 (4.9)

aromatic

alkane

alkene

0

20

40

60

80

100

60 120 180

Sel

ecti

vit

y o

f ker

ose

ne

ran

ge

hyd

roca

rbo

ns

(%)

Reaction time (min)

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Temperature is an operating parameter affecting hydrocracking

catalysts activity which is evaluated by the degree of deoxygenation and degree of

cracking expressed in corresponding Eqs. (4.8) and (4.9). The degree of cracking (DOC)

and degree of deoxygenation (DOD) of waste virgin coconut oil for the HZSM5 at the

reaction temperature range of 350°C and 400°C are presented in Figures 4.20 and 4.21,

respectively. As increasing the reaction temperature from 350°C to 400°C, the DOD was

increased to 11.99 % or by a factor of 1.31 (Figure 4.20) and the DOC was increased to

13.59 % or by a factor of 1.62 (Figure 4.21 ). This was attained that the amount of

triglyceride are more cracked to light products by increasing reaction temperature

(Gutierrez et al., 2012).

Figure 4.20 The Effect of the reaction temperature on the degree of deoxygenation

over HZSM-5 catalysts

5.18

8.13

11.99

0

5

10

15

20

340 350 360 370 380 390 400 410

Deg

ree

of

Deo

xygen

atio

n [

DO

D]

Reaction temperatre [°C]

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Figure 4.21 The effect of the reaction temperature on the degree of cracking on over

HZSM-5 catalysts

Since the presence of hydrogen is insufficient to avoid coke

formation resulting in deactivation of the catalysts, it is needed to split off the fatty

acids from the glycerides for the further reactions (Xu et. al., 2010). In Figures 4.22 and

4.23, the effects of initial hydrogen pressure ranging from 20 to 40 bar on the DOC and

the DOD of waste virgin coconut oil for the HZSM-5 catalysts are presented. The result

showed that initial hydrogen pressure had negligible effect on the degree of

deoxygenation and degree of cracking.

5.18

8.75

13.59

0

5

10

15

20

340 350 360 370 380 390 400 410

Deg

ree

of

crac

kin

g [

DO

C]

Reaction temperature [°C]

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Figure 4.22 The effect of the initial hydrogen pressure on the degree of

deoxygenation on over HZSM-5 catalysts

Figure 4.23 The effect of the initial hydrogen pressure on the degree of cracking on

the over HZSM-5 catalysts

11.20 11.5911.99

0

5

10

15

20

15 20 25 30 35 40 45

Deg

ree

of

Deo

xygen

atio

n [

DO

D]

Initial hydrogen pressure [bar]

12.50 12.6413.59

0

5

10

15

20

15 20 25 30 35 40 45

Deg

ree

of

crac

kin

g [

DO

C]

Initial hydrogen pressure [bar]

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In general, as the reaction proceeds, the content of liquid

hydrocarbon in products increases, following by drastic increase of the DOC to 33.58

% as shown in Figure 4.24 . The DOD also was increased to 31.16 % as the reaction

time increased (Figure 4.25 resulting in formation of non-deoxygenated liquid product.

Figure 4.24 The effect of the reaction time on the degree of deoxygenation over

HZSM-5 catalysts

Figure 4.25 The effect of the reaction time on the degree of cracking over HZSM-5

catalysts

11.9910.06

31.16

0

5

10

15

20

25

30

35

40 60 80 100 120 140 160 180 200

Deg

ree

of

deo

xygen

atio

n [

DO

D]

Reaction time [min]

13.5912.16

33.58

0

5

10

15

20

25

30

35

40 90 140 190

Deg

reee

of

crac

kin

g [

DO

C]

Reaction time [min]

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4.8 Continuous process

4.8.1 Experimental

The continuous hydrocracking lab-scale process of waste virgin

coconut oil was performed in a fixed bed reactor as shown in Figure 4. 26 . A 0.1 gram

of HZSM-5 catalyst was packed in the fixed bed reactor column and the hydrocracking

temperature cannot be exceeded the upper temperature limit of 350°C. The effect of

hydrogen flow rate was varied between 20 ml/min and 50 ml/min at the feedstock

flow rate of 0.06 ml/min. The fixed bed column length and fixed-bed column diameter

were 10 cm and 0.18 inch (0.4572 cm), respectively. The amount of waste virgin

coconut oil was flowed together with hydrogen in to the laboratory-scale continuous

reactor packed with the prepared HZSM-5 catalyst.

Figure 4.26 Reactor set-up

4.8.2 Product Analysis

The reactions were conducted for 30 to 90 mins. The products were

collected and analyzed by using GC/MS (Model: 7890B, Agilent Technologies, USA). In

this study, the gas product and coke yield were undetermined. The decanoic acid (DA)

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as a rich feed. The calculation of conversion was based on the amount of decanoic

acid (C10H20O2) in feed and in product as expressed in Eq. (4.10).

𝐶𝑜𝑛𝑣𝑒𝑟𝑠𝑖𝑜𝑛 (%) = 𝑑𝑒𝑐𝑎𝑛𝑜𝑖𝑐 𝑎𝑐𝑖𝑑𝑓𝑒𝑒𝑑−𝑑𝑒𝑐𝑎𝑛𝑜𝑖𝑐 𝑎𝑐𝑖𝑑𝑝𝑟𝑜𝑑𝑢𝑐𝑡

𝑑𝑒𝑐𝑎𝑛𝑜𝑖𝑐 𝑎𝑐𝑖𝑑𝑓𝑒𝑒𝑑 𝑥 100 (4.10)

At a variation of hydrocracking hydrogen feed rate, decanoic acid

conversion was examined and reported in Figure 4.27. The conversion of decanoic acid

was between 91 to 99 % with the various the hydrogen flow rate range of 20 to 50

ml/min.

Figure 4.27 Decanoic acid conversion over HZSM-5 as function of time

4.8.3 Effect of hydrogen flow rate

Hydrogen flow rate which serves as the reactant is also used as a

carrier gas. Hydrogen flow rate is inversely proportional to the residence time of

reactant molecules on the surface of the catalyst. Thus, the higher the flow rate, the

shorter the residence time of reactant molecules on the surface of the catalyst.

0

20

40

60

80

100

30 60 90

Conver

sion (

%)

reaction time (minutes)

20 ml/min

30 ml/min

40 ml/min

50 ml/min

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The hydrogen flow rate ranging from 20 to 50 ml/min significantly

affected the yield of bio-kerosene fraction at the reaction time of 30 mins as shown in

Figure 4.28. The fraction of bio-kerosene produced from the HZSM-5 catalyzed cracking

reaction of waste virgin coconut oil has the opposite trend to the formation of the bio-

gasoline fraction. The produced bio-kerosene fraction increased from 0.40% to 9.04%

with increasing flow rate up to 40 ml/min. Further increase of the hydrogen gas flow

rate to 50 mL/min, the amount of bio-kerosene fraction decreased. This may be

attributed that the hydrogen flow rate higher than 40 ml/min enhanced secondary

cracking and lighter product formation.

Figure 4.28 The effect of the hydrogen flow rate on product formation at the reaction

time 30 minutes

The result shows no significant changes in bio-gasoline fraction

product when increasing the reaction time to 60 minutes and increasing the hydrogen

flow rate as shown in Figure 4.29, the highest bio-kerosene was 15.27% at the hydrogen

0.57

0.00 0.00

5.00

0.40

4.81

9.04

0.47

3.58

0.00 0.00

2.71

0

1

2

3

4

5

6

7

8

9

10

0 10 20 30 40 50 60

Yie

ld [

%]

Hydrogen flow rate [ml/min]

Reaction time 30 min gasoline

kerosene

>C13

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flow rate of 50 ml/min. Thus, the hydrogen flow rate of 50 ml/min and the reaction

time of 60 minutes are the most appropriate condition for formation of bio-kerosene

range product.

The effect of the hydrogen flow rate ranging from 20 to 50 ml/min

was studied by increasing the reaction time up to 90 minutes as shown in Figure 4.30.

The formation of products in the range of bio-gasoline and bio-kerosene was not

observed, although the hydrogen flow rate increased. This may be attributed that

longer reaction time causes the catalyst deactivated at the longer reaction time.

Figure 4.29 The effect of the hydrogen flow rate on product formation at the reaction

time 60 minutes

0.000.00

0.00 0.00

11.40

0.052.39

20.68

14.41

6.90

0.00

5.29

0

5

10

15

20

25

0 10 20 30 40 50 60

Yie

ld (

wt%

)

Hydrogen flow rate [ml/min]

Reaction time 60 mingasoline

kerosene

>C13

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Figure 4.30 The effect of the hydrogen flow rate on product formation at the reaction

time 90 minutes

4.8.4 Effect of reaction time on catalyst activity and selectivity to

product

Cracking reactions with variation of reaction time were performed at

a hydrogen flow rate of 50 ml/min since this flow rate was capable of producing the

highest fraction of kerosene. The fraction of bio-kerosene was increased from 0.43 %

to 20.68 % with increasing the reaction time up to 60 minutes. After 60 minutes of

reaction time, the kerosene fraction significantly decreased to 0.80 %. Furthermore at

the increase of the reaction time, the gasoline fraction decreased while the heavy

fraction (>C13) increased. The prolonged reaction time probably caused a decrease in

catalyst activity due to coke deposition covering the active site of the catalyst.

0.27

0.00 0.000.00

2.42

1.430.68 0.80

17.41

0.67

0.00

4.13

0

2

4

6

8

10

12

14

16

18

20

0 10 20 30 40 50 60

Yie

ld (

wt%

)

Hydrogen flow rate [ml/min]

Reaction time 90 min

gasoline

kerosene

>C13

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Figure 4.31 The effect of a reaction time with the hydrogen flow rate 50 ml/min

The effect of hydrogen flow rate on the selectivity to product at a

variation of the reaction time was shown Figures 4.32 -4.34 . A biofuel selectivity is

defined in Eq. (4.10)

𝑆𝑒𝑙𝑒𝑐𝑡𝑖𝑣𝑖𝑡𝑦(𝐶𝑥𝐻𝑦) (%) = (𝐶𝐻)𝑛𝑝𝑟𝑜𝑑𝑢𝑐𝑡𝑠

∑(𝐶𝐻)𝑛𝑝𝑟𝑜𝑑𝑢𝑐𝑡𝑠 𝑥 100 (4.10)

With increasing the hydrogen flow rate from 20 to 50 ml/min at the

reaction time 30 minutes, the gasoline selectivity reached 58.60 % and then decreased

sharply at the reaction time 60. As increasing the reaction time to 60 and 120 minutes,

the main product components were in the range of kerosene.

5.00

0.000.00

0.47

20.68

0.80

2.71

5.294.13

0

5

10

15

20

25

0 20 40 60 80 100

Yie

ld (

wt%

)

Progress of reaction[min]

gasoline

kerosene

>C13

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Figure 4.32 The effect of hydrogen flow rate on the selectivity to product at 30

minutes

Figure 4.33 The effect of hydrogen flow rate on the selectivity to product at 60

minutes

gasoline

kerosene

diesel

0

20

40

60

80

100

20 30 40 50

Sel

ecti

vit

y (

wt%

)

Hydrogen flow rate (ml/min)

reaction time 30 minutes

gasoline

kerosene

diesel

0

20

40

60

80

100

20 30 40 50

Sel

ecti

vit

y (

wt%

)

Hydrogen flow rate (ml/min)

reaction time 60 minutes

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Figure 4.34 The effect of hydrogen flow rate on the selectivity to product at 120

minutes

gasoline

kerosene

diesel

0

20

40

60

80

100

20 30 40 50

Sel

ecti

vit

y (

wt%

)

Hydrogen flow rate (ml/min)

reaction time 120 minutes

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CHAPTER V

CONCLUSION AND RECOMMENDATIONS

5.1 Conclusion

The performance of zeolite (HZSM-5) catalysts was prepared for the

hydrocracking of waste virgin coconut oil to produce gasoline, kerosene (Jet fuel) and

diesel range in a laboratory-scale batch reactor. The operating parameters were a

temperature range of 350 to 400ºC, operating pressure range of 20 to 40 bar and

reaction time range of 1 to 3 h.

Our findings can be concluded as the followings.

1.The increase of the reaction temperature favoured hydrocracking process to

light hydrocarbon products such as kerosene and gasoline while it did not favor

hydrocracking process to heavy hydrocarbon product such as diesel. Pressure

dependence on yields of biofuels derived from hydrocracking of waste virgin coconut

oil was insignificant.

2. Longer time favoured hydrocracking process to lighter fraction products such

as gasoline and kerosene. On the conversely, diesel production was not favoured by

longer time operation.

3. Based on the experiments, the highest yield of gasoline and kerosene was

obtained when the operated condition were 400°C, 40 bar, and 3 h and the operated

condition at 350°C, 40 bar, and 1 h gave the highest yield of diesel.

4. Strength relationships among the three operating parameters using the

Pearson’s correlation coefficients showed strong dependence of reaction temperature

and time on Ygasoline and Ykerosene, but strong adverse relationship with Ydiesel.

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5.2 Recommendations

The recommendations for further study are listed as follows:

1. Initial hydrogen pressure was responsible for the steps of catalytic cracking

and hydrogenation. Based on the experiments, the effect of initial hydrogen pressure

has been studied in the range between 20 and 40 bar and the result found that the

initial hydrogen pressure has not only weakly affected but also no significant effect

observed on the yields of biofuel. It is recommended that hydrogen pressure higher

than 40 bar should be studied in further work.

2. The result suggests that hydrocracking reactions are favoured at higher

temperatures since the liquid products are breaking down to form more gas products.

In this work the highest operating temperature was 400°C that improved the yield of

kerosene and gasoline. It is recommended that the temperature range between 400-

500°C for biofuel production should be studied in further work.

3. A comprehensive kinetic model and reaction mechanisms for hydrocracking

process of waste virgin coconut oil should be developed for large-scale production

and optimization of hydrocracking process.

Chemical Reaction Model

The applied rates of reactions in hydrocracking process are expressed as follows:

−𝑟𝑓𝑒𝑒𝑑 = 𝐾𝐶𝑓𝑒𝑒𝑑

where K and 𝐶𝑓𝑒𝑒𝑑 are reaction rate constant and feed concentration, respectively.

The reaction constant can be estimated by Arrhenius equation as follows:

𝐾 = 𝐴𝑒𝑥𝑝(−𝐸𝑎

𝑅𝑇)

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REFERENCES

Book and Book Articles

Bin, X. (2007). Structure-performance relationships in solid-acid aluminosilicates. The

United Kingdom: PhD thesis, University of York.

Gervajio, G. C. (2005). Fatty Acids and Dervatives from Coconut Oil.

Hobson, G. D. (1984). Modern Petroleum Technology. Michigan: Wiley Chichester.

Mahmud, H. (1998). Catalytic cracking of Palm Oil to Liquid Fuels over Various Y-

Type Zeolites. Universiti Teknologi Malaysia: Master Thesis.

Mueller, V. H. (2013). Rational Catalyst Design for Direct Conversion of CH4 and CO2.

Washington: Washington University in St. Louis.

Scherzer, J. (1990). Octane-Enhancing Zeolite FCC Catalysts. New York: Marcel

Dekker.

Scherzer, J., & Gruia, A. (1996). Hydrocracking Science and Technology. CRC Press.

Siregar, T. B. (2005). Catalytic Cracking Palm Oil Gasoline Using Zeolite Catalysts.

Universiti Teknologi Malaysia.

Smart, L., & Moore, E. (1992). Solid State Chemistry, an Introduction. London:

Chapman and Hall.

Speight, J. G., & Ozum, B. (2000). Petroleum Refining Processes. Taylor&Francis.

Articles

Adjaye, J., & Bakhshi, N. (1995). “Production of hydrocarbons by catlytic upgrading of

a fast pyrolysis bio-oil. Part I: Conversion over various catalysts”. Fuel

Processing Technology, 45(3), 161-183.

Ref. code: 25605810030592YLH

Page 94: PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE …ethesisarchive.library.tu.ac.th/thesis/2017/TU... · yields of biofuel production by hydroconversion of waste virgin coconut oil

75

Al-Sabawi, M., & Chen, J. (2012). “Hydroprocessing of Biomass-Derived Oils and Their

Blend with Petroleum Feedstocks”: A Review. Energy Fuels, 26(9), 5373-5399.

Anand, M., Farooqui, S. A., Kumar, R., Joshi, R., Kumar, R., Sibi, M. G., Sinha, A. K.

(2016). “Optimizing renewable oil hydrocracking consitions for aviation bio-

kerosene production”. Fuel Processing Technology, 151, 50-58.

Arida, V., Usita, M., Angeles, M., Hernadez, C., & Manalo, L. (1986). “Production of

Petroleum Fuel Substitutes by Catalytic Cracking of Coconut Oil”. Proceedings

of Asean Conference on Energy from Biomass, (pp. 1-13). Penang.

Bezergianni, S., Dimitriadis, A., Kalogianni, A., & Pilavachi, P. (2010). “Hydrotreating of

waste cooking oil for biodiesel production. Part I: Effect of temperature on

prooduct yields and heteroatom removal”. Bioresoure Technology, 101(17),

6651-6656.

Bezergianni, S., Dimitriadis, A., Sfetsas, T., & Kalogianni, A. (2010). “Hydrotreating of

waste cooking oil for biodiesel production. Part II: effect of temperature on

hydrocarbon composition”. Bioresource Technology, 101(19), 7658-7660.

Bezergianni, S., Voutetakis, S., & Kalogianni, A. (2009). “Catalytic Hydrocracking of

Fresh and Used Cooking Oil”. Ind. Eng. Chem. Res., 48, 8402-8406.

Bezergianni, S., & Dagonikou, V. (2015). “Effect of CO2 on catalytic hydrotreatment of

gas-oi”l. The canadian journal of chemical engineering, 93(6), 1017-1023.

Bhatia, S., Kee, H., Lan, L., & Mohamed, A. (1998). “Production of bio-fuel by catalytic

cracking of palm oil: Performance of different catalysts”. Proceedings of the

Biofuel, PORIM International Biofuel and Lubricant Conference, (pp. 107-112).

Budianto, A., Prajitno, D. H., Roesyadi, A., & Budhikarjono, K. (2014). “HZSM-5 catalyst

for cracking palm oil to biodiesel: a comparative study with and without Pt

and Pd impregnation”. Scientific Study & Research, 15(1), 081-090.

Busca, G. (2007). “Acid Catalyts in Industrial Hydrocarbon Chemistry”. Chemical

Reviews, 107(11), 5366-5410.

Ref. code: 25605810030592YLH

Page 95: PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE …ethesisarchive.library.tu.ac.th/thesis/2017/TU... · yields of biofuel production by hydroconversion of waste virgin coconut oil

76

Can, L., Jing, L., Gang, Z., Weiqian, T., & Long, R. (2013). “A cleaner process for

hydrocracking of jatropha oil into green diese”l. Journal of the Taiwan

Institute of Chemical Engineers, 44, 221-227.

Chang, W., & Tye, C. (2013). “Catalytic cracking of used palm oil using composite

zeolite”. The Malaysian Journal of Analytical Sciences, 17(1), 176-184.

Charusiri, W., Yongchareon, W., & Vitidsant, T. (2006). “Conversion of used vegetable

oils to liquid fuels and chemicals over HZSM-5, sulfated zirconia and hybrid

catalysts”. Korean Journal of Chemical Engineering, 23(3), 349-355.

Corma, A. (1995). “Inorganic Solid Acids and Their Use in Acid-Catalyzed Hydrocarbon

Reactions”. Chemical Reviews, 95(3), 559-614.

Csicsery, S. M. (1984). “Shape-selective catalysis in zeolites”. Zeolites, 4(3), 202-213.

Dayrit, F. M., Dimzon, I. D., Valde, M. F., Santos, J. R., Garrovillas, M. M., & Villarino, B.

J. (2011). “Quality characteristics of virgin coconut oil: Comparisons with

refined coconut oil”. Pure and Applied Chemistry, 83(9), 1789-1799.

Donnis, B., Egeberg, R., Blom, P., & Knudsen, K. (2009). “Hydroprocessing of Bio-oils

and oxygenates to hydrocarbons: understanding the reaction routes”. Topics

in Catalysts, 52(3), 229-240.

Flanigen, E. (1980). “Molecular sieve zelite technology - the first twenty-five years”.

Pure and Applied Chemistry, 52(9), 2191-2211.

Garcia, L., Benedicto, A., Romeo, E., Salvador, M., Arauzo, J., & Bilbao, R. (2002).

“Hydrogen Production by Steam Gasification of Biomass Using Ni-Al

Coprecipitated Catalysts Promoted with Magnesium”. Energy Fuels, 16(5),

1222-1230.

Gutierrez, A., Castano, P., Arandes, J. M., & Bilbao, J. (2012). “Effect of temperature in

hydrocracking of light cycle oil on a noble metal-supported catalyst for fuel

production”. Chemical Engineering & Technology, 35, 653-660.

Ref. code: 25605810030592YLH

Page 96: PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE …ethesisarchive.library.tu.ac.th/thesis/2017/TU... · yields of biofuel production by hydroconversion of waste virgin coconut oil

77

Hafshah, H., Prajitno, D. H., & Roesyadi, A. (2017). “Hydrotalcite Catalyst for

Hydrocracking Calophyllum inophyllum Oil to Biofuel: A Comparative study

with and without Nickel Impregnation”. Bulletin of Chemical Reaction

Engineering&Catalysis, 12(2), 273-280.

Hanafi, S., Elmelawy, M., El-Syed, H., & Shalaby, N. H. (2015). “Hydrocracking of Waste

Cooking Oil as Renewable Fuel on NiW/SiO2/Al2O3 Catalyst”. Journal of

Advanced Catalysis Science and Technology, 2, 27-37.

Huber, G., & Corma, A. (2007). “Synergies between Bio- and Oil refineries for the

production of fuel biomass Angewandte”. Biorefineries, 46, 7184-7201.

Idem, R., Katikaneni, S., & Bakhshi, N. (1997). “Catalytic Conversion of Canola Oil to

Fuels and Chemicals: Roles of Catalyst Acidity, Basicity and Shape Selective

on Product Distribution”. Fuel Processing Technology, 51, 101-125.

Ishihara, A., Fukui, N., Nasu, H., & Hashimoto, T. (2014). “Hydrocracking of soybean oil

using zeolite-alumina composite supported NiMo catalysts”. Fuel, 134, 611-

617.

Information Nigeria. (2016). Retrieved from http://www.informationng.com

John A. Dutton. (2018). “Terminology for vegetable oils and animal fats”. Retrieved

from http://www.e-education.psu.edu

Kappally, S., Shirwaikar, A., & Shirwaikar, A. (2015). “Coconut oil-a review of potential

applications”. Hygeia journal for drugs and medicines, 7(2), 34-41.

Kiatkittipong, W., Phimsen, S., Kiatkittipong, K., Wongsakulphasatch, S., Laosiripojana,

N., & Assabumrungrat, S. (2013). “Diesel-like hydrocarbon production from

hydroprocessing of relevant refining palm oil”. Fuel Processing Technology,

116, 16-26.

Kim, S., Brand, S., Lee, H., Kim, Y., & Kim, J. (2013). “Production of renewable diesel

by hydrotreatment of soybean oil: Effect of reaction parameters”. Chemical

Engineering Journal, 228, 114-123.

Ref. code: 25605810030592YLH

Page 97: PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE …ethesisarchive.library.tu.ac.th/thesis/2017/TU... · yields of biofuel production by hydroconversion of waste virgin coconut oil

78

Kim, S., Han, J., Lee, H., Yum, T., Kim, Y., & Kim, J. (2014). “Production of renewable

diesel via catalytic deoxygenation of natural triglycerides: Comprehensive

understanding of reaction intermediates and hydrocarbons”. Applied Energy,

116, 199-205.

Kimura, T., Imai, H., Li, X., & Khattaf, S. a. (2016). “Hydroconversion of triglycerides to

hydrocarbons over Mo-Ni/γ-Al2O3 catalyst under low hydrogen pressure”.

Catalysis Letters, 1(143), 1175-1181.

Kimura, T., Imai, H., Li, X., Sakashita, K., Asaoka, S., & Al-Khattaf, S. S. (2013).

“Hydroconversion of Triglycerides to Hydrocarbons Over Mo-Ni/-Al2O3

Catalyst Under Low Hydrogen Pressure”. Catalysis Letters, 143, 1175-1181.

Kubicka, D., & Kaluza, L. (2010). “Deoxygenation of vegetable oils over sulfide Ni, Mo

and NiMo catalysts”. Applied Catalysis, 372(2), 199-208.

Kumar, P., Yenumala, S. R., & Maity, S. K. (2014). “Kinetics of hydrodeoxygenation of

steric acid using supported nickel catalysts: Effects of supports”. Applied

Catalysis A: General, 471, 28-38.

Liu, Y., Sotelo-Boyas, R., Murata, K., Minowa, T., & Sakanishi, K. (2012). “Production of

Bio-Hydrogenated Diesel by Hydrotreatment of Hight-Acid-Value Waste

Cooking Oil over Ruthenium Catalyst Supported on Al-Polyoxocation-Pillared

Montmorillonite”. Catalysts, 2, 171-190.

Maki-Arvela, P., Kubickova, I., Snare, M., Eranen, K., & Murzin, D. (2007). “Catalytic

deoxygenation of fatty aacids and their derivatives”. Energy Fuels, 21, 30-41.

Marlinda, L., Al-Muttaqii, M., Gunardi, I., Roesyadi, A., & Prajitno, D. H. (2017).

“Hydrocracking of Cerbera manghas oil with Co-Ni/HZSM-5 as double

promoted catalyst”. Bulletin of Chemical Reaction Engineering & Catalysis,

12(2), 167-184.

Marlinda, L., Al-Muttaqii, M., Roesyadi, A., & Prajitno, D. H. (2016). “Production of

biofuel by hydrocracking of Cerbera Manghas Oil using Co-Ni/HZSM-5 catalyst:

Ref. code: 25605810030592YLH

Page 98: PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE …ethesisarchive.library.tu.ac.th/thesis/2017/TU... · yields of biofuel production by hydroconversion of waste virgin coconut oil

79

effect of reaction tempertaure”. Journal of pure and applied chemistry

research, 5(3), 189-195.

Mills, G., Heinemann, H., Milliken, T., & Oblad, A. (1953). “Naphtha reforming involves

dual functioal catalysts-mechanism for reforming with these catalysts”. Ind.

Eng. Chem, 45, 124.

Mohammad, M., Hari, T. K., Yaakob, Z., Sharma, Y. C., & Sopian, K. (2013). “Overview

on the production of paraffin based-biofuels vua catalytic

hydrodeoxygenation”. Renewable and Sustainable Energy Reviews, 22, 121-

132.

Moissette, A., Hureau, M., Tzanis, L., & Daou, T. J. (2017). “Effects of the zeolite

particle size on the charge separated states”. 254, Elsevier BV.

Muhammad, M. A., Roesyadi, A., Marlinda, L., & Prajitno, D. H. (2017). “Co-Ni/HZSM-5

catalyst fro hydrocracking of Sunan Candlenut Oil for production of biofuel”.

Pure App. Chem. Res., 6(2), 1-10.

Mustafa Al Bakri, A., Kamarudin, H., Bnhussain, M., Nizar, I. K., Rafiza, A., & Zarina, Y.

(2012). “The processing, characterization, and properties of fly ash based

geopolymer concrete”. Reviews on advanced materials science, 30, 90-97.

Marcus, Bonnie K. and Cormier, William E., (1999). "Going Green with

Zeolites", Chemical Engineering Progress, June, SRI consulting's website,

"Process Economics Program"

Nasikin, M., Susanto, B. H., Hirsaman, M. A., & Wijanarko, A. (2009). “Biogasoline from

Palm Oil by Simultaneous Cracking and Hydrogenaion Reaction over

Nimo/zeolite Catalyst”. World Applied Science Journal, 5, 74-79.

Neuling, U., & Kaltschmitt, M. (2018). “Techno-economic and environmental analysis

of aviation biofuels”. Fuel Processing Technology, 171, 54-69.

Ref. code: 25605810030592YLH

Page 99: PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE …ethesisarchive.library.tu.ac.th/thesis/2017/TU... · yields of biofuel production by hydroconversion of waste virgin coconut oil

80

Nimmanterdwong, P., Piumsomboon, P., & Chalermsinsuwan, B. (2015). “Emergy

evaluation of biofuels production in Thailand from different feedstocks”.

Ecological Engineering, 74, 423-437.

Oliveira, C. F., Dezaneti, L. M., Garcia, F. A., Macedo, J. L., Dias, J. A., Dias, S. C., &

Alvim, K. S. (2010). “Esterification of oleic acid with ethanol by 12-

tungstophosphoric aicd supported on zirconia”. Applied Catalysis A: General,

372(2), 153-161.

Rahman, M. M., Abu-Zied, B. M., & Asiri, A. M. (2017). “Ultrasensitive hydrazine sensor

fabrication based on Co-doped ZSM-5 zeolites for environmental safety”.

Royal society of chemistry, 7, 21164-21174.

Rasyid, R., Prihartantyo, A., Mahfad, M., & Roesyadi, A. (2015). “Hydrocracking of

calophyllum inophyllum oil with non-sulfide CoMo catalysts”. Bulletin of

Chemical Reaction Engineering & Catalysis, 10(1), 61-69.

Salam , B., Ani, F., & Islam, M. (1996). “Fixed Bed Catalytic Upgrading of Crude Palm

Oil by HZSM-5 Catalyst”. Proceedings of Regional Symposium on Chemical

Engineering, 350-357, Bangi, Selangor, Malaysia: The 12th Symposium of

Malaysian Chem. Engineer. Retrieved July 9-10, 1996

Salim, l., Trisunaryanti, W., Triyono, & Arryanto, Y. (2016). “Hydrocracking of Coconut

Oil into Gasoline Fraction using NI/Modified Natural Zeolite Catalyst”.

International Journal of ChemTech Research, 9(4), 492-500.

Salwa, A., Samia, A., Mohamed, M., & Eslam, F. A. (2015). “Hydrocracking of Jojoba for

green fuel production”. Journal of Petroleum Science and Technology, 5(2),

59-69.

Satyarthi, J., Chiranjeevi, T., Gokak, D., & Viswanathan, P. (2013). “An overview of

catalytic conversion of vegetable oils/fats into middle distillates”. Catalysis

Science & Technology, 3(1), 70.

Ref. code: 25605810030592YLH

Page 100: PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE …ethesisarchive.library.tu.ac.th/thesis/2017/TU... · yields of biofuel production by hydroconversion of waste virgin coconut oil

81

Simacek, P., Kubicka, D., Sebor, G., & Pospisil, M. (2009). “Hydroprocessed rapeseed

oil as a source of hydrocarbon-based biodiesel”. Fuel, 88(3), 456-460.

Sinfeld, J. (1983). Bimetalic Catalyts: DIscoveries, Concepts and Applications.

Newyork: Wiley.

Sirajudin, N., Jusoff, K., Yani, S., Ifa, L., & Roesyadi, A. (2013). “Biofuel Production from

Catalytic Cracking of Palm Oil”. World Applied Sciences Journal, 26, 67-71.

Sotelo-Boyas, R., Liu, Y., & Minowa, T. (2008). “Production of green diesel by

hydrocracking of canola oil on Ni-Mo/γ-Al2O3 and Pt-Zeolitic based catalyts”.

1, 1-9. AlChE Annual Meeting.

Sotelo-Boyas, R., Liu, Y., & Minowa, T. (2011). “Renewable Diesel Production from the

Hydrotreating of Rapeseed Oil with Pt/Zeolite and NiMo/Al2O3 Catalysts”.

Industrial&Engineering Chemistry Research, 50(5), 2791-2799.

Srifa, A., Faungnawakij, K., Itthibenchapong, V., Viriya-Empikul, N., Charinpanitkul, T., &

Assabumrungrat, S. (2014). “Production of bio-hydrognated diesel by catalytic

hydrotreating of palm oil over NiMoS2/-Al2O3 catalyst”. Bioresource

Technology, 158, 81-90.

Twaiq, F., Zabidi, N., & Bathia, S. (1999). “Catalytic Conversion of Palm Oil to

Hydrocarbons: Performance of Various Zeolite Catalysts”.

Industrial&Engineering Chemistry Research, 38(9), 3230-3237.

Roxas Sigma Agriventures, Inc. (2016). Retrieved from http://www.roxassigmaagri.com

Veriansyah, B., Han, J., Kim, S., Hong, S., Kim, Y., Lim, J., Kim, J. (2012). “Production of

renewable diesel by hydroprocesing of soybean oil: Effect of catalysts”. Fuel,

94(1), 578-585.

Verma, D., Rana, B. S., Kumar, R., Sibi, M., & Sinha, A. K. (2016). “Diesel and aviation

kerosene with desired aromatics from hydroprocessing of jatopha oil over

hydrogenation catalysts supported on hierarchical mesoporous SAPO-11”.

Applied Catalysis A: General, 490, 108-116.

Ref. code: 25605810030592YLH

Page 101: PRODUCTION OF BIOFUEL BY HYDROCONVERSION OF WASTE …ethesisarchive.library.tu.ac.th/thesis/2017/TU... · yields of biofuel production by hydroconversion of waste virgin coconut oil

82

Villarino, B. J., Dy, L. M., & Lizada, M. C. (2007). “Descriptive sensory evaluation of

virgin coconut oil and refined, bleached and deodorized coconut oil”. Food

Science and Technology, 40(2), 193-199.

Weisz, P., Frilette, V., Maatman, R., & Mower, E. (1962). “Catalysis by crystalline

aluminosilicates II. Molecular-shape selective reactions”. Journal of Catalysis,

1(4), 307-312.

Xu, J., Jiang, J., Chen, J., & Sun, Y. (2010). “Biofuel production from catalytic cracking

of woody oils”. Bioresource Technology, 101(14), 5586-5591.

Yang, S., Lin, J., Guo, D., & Liaw, S. (1999). “1-Butene isomerization over

aluminophosphate molecular sieves and zeolites”. Applied Catalysis A:

General, 181(1), 113-122.

Yilmaz, N., & Atmanli, A. (2017). “Sustainable alternative fuels in aviation”. Energy,

140, 1378-1386.

Zaher, F. A., El Sayed, H. A., Heakal, B. H., & Hamed, S. F. (2015). “Potential of castor

oil as a feedstock for the production of bio-fuel via catalytic hydrocracking”.

Current Science International, 4(3), 443-449.

Zandonai, C. H., Yassue-Cordeiro, P. H., Berenice, S., Pergher, C., Olsen Scaliante, M.

N., & Fernandes-Machado, C. N. (2016). “Production of petroleum-like

synthetic fuel by hydrocracking of crude soybean oil over ZSM-5 zeolite -

Improvement of catalyst lifetime by ion exchange”. Fuel, 172, 228-237.

Zhang, Y., Dube, M., McLean, D., & Kates, M. (2003). “Biodiesel production from waste

cooking oil: 1. Process design and technological assessment”. Bioresource

Technology, 89, 1-16.

Zhao, X., Wei, L., Cheng, S., Huang, Y., Yu, Y., & Julson, J. (2015). “Catalytic cracking of

camelina oil for hydrocarbon biofuel over ZSM-5-Zn catalyst”. Fuel Processing

Technology, 139, 117-126.

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APPENDICES

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APPENDIX A

RAW DATA OF CHARACTERIZATION

APPENDIX A.1: Raw data of gas chromatography-mass spectrometry

Table A.1

Compositional analysis of low-grade waste virgin coconut oil

Fatty acid composition Compound

Formula Retention time

(min) wt%

C8:0 Caprylic acid C8H16O2 8.493 15.65

C10:0 Capric acid C10H20O2 10.08 11.19

C12:0 Lauric acid C12H24O2 12.275 58.79

C14:0 Myristic acid C14H28O2 15.234 14.38

Table A.2

Compositional analysis of high-grade waste virgin coconut oil

Fatty acid composition Compound

formula

Retention time

(min) wt%

Cyclohexanecarboxylic acid C7H12O2 10.60 1.30

Nonenoic acid C9H16O2 8.88 1.18

Capric acid C10H20O2 10.97 51.15

Undecylic acid C11H22O2 16.66 34.02

Dodecenoic acid C12H22O2 13.06 0.30

Lauric acid C12H24O2 21.00 12.05

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APPENDIX A.2: Condition of Gas Chromatography-Mass Spectrometry

APPENDIX A.2.1: Condition of Gas Chromatography-Mass Spectrometry (GC-MS) for

reactant (high-grade waste virgin coconut oil)

GC

Model Agilent Technologies 7890B

Mode of Injection

Liquid/Split 20:1

Injection volumn

2.0 µL

Injection temperature

250°C

GC Column HP-Innowax

GC Oven Rate(°C/min) Value (°C) Hold time

(min) Run time (min)

50 1 1

25 200 0 7

3 230 23 40

MS

Model

Agilent

Techologies

5977A

Ion Source EI

Source Temp. 230 °C

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APPENDIX A.2.2: Condition of Gas Chromatography-Mass Spectrometry (GC-MS) for

liquid products (Batch process)

GC

Model

Agilent

Technologie

s 7890B

Mode of

Injection

Liquid/Split

50:1

Injection

volumn 0.5 µL

Injection

temperature 220°C

GC Column HP-5MS

GC Oven Rate(°C/min) Value (°C) Hold time

(min) Run time (min)

35 10 10

10 200 10 36.5

Quad Temp. 150 °C

Fixed Electron E. 70 eV

Acquisition Type Scan

Start Mass (m/z) 46 End Mass

(m/z) 500

Frequency

(scans/sec) 4.4

Solvent Cut

Time (min) 1.6

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MS

Model

Agilent

Techologies

5977A

Ion Source EI

Source Temp. 230 °C

Quad Temp. 150 °C

Fixed Electron

E. 70 eV

Acquisition

Type Scan

Start Mass

(m/z) 10

End Mass

(m/z) 600

Frequency

(scans/sec) 2.5

Solvent Cut

Time (min) 3.6

APPENDIX A.2.3: Condition of Gas Chromatography-Mass Spectrometry (GC-MS) for

liquid products (Continuous process)

GC

Model

Agilent

Technologies

7890B

Mode of Injection Liquid/Split

20:1

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Injection volumn 0.5 µL

Injection

temperature 250°C

GC Column HP-5MS

GC Oven Rate(°C/min) Value (°C) Hold time (Min) Run time (Min)

35 10 10

10 300 5 30

MS

Model Pegasus 4D-

C, Leco,USA

Ion Source EI

Source Temp. 300°C

Quad Temp. 230°C

Fixed Electron E. 70 eV

Acquisition Type Scan

Start Mass (m/z) 46 End Mass

(m/z) 500

Frequency

(scans/sec) 4.4

Solvent

Cut Time

(min)

4

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APPENDIX A.3: XRD Analysis

Table A.3

Data of Theta and six highest peaks of zeolite and H-zeolite

Catalyst Theta FWHM (deg) Particle size (nm) Average particle

size (nm)

HZSM-5 7.924 0.148 56.24 18.34

8.315 4.089 2.04

22.675 0.442 19.46

23.127 1.168 7.26

23.154 0.394 21.51

24.409 2.221 3.83

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APPENDIX A.4: Temperature programmed desorption of ammonia

Table A.4

Raw data of temperature programmed desorption of ammonia

Pretreatment Parameters

Number of pretreatment step 6

Sample weight 0.0569 g

STEP Gas name Flow rate (ml/min) Time (min) Target temperature (ºC)

1 He 50 50 500

2 He 50 60 500

3 He 50 1 100

4 He 50 10 100

5 NH3/He 50 30 100

6 He 50 15 100

Measurement Condition

Time for detector stabilization 20

Target temperature 610

Ramp rate 10

Target temperature holding time 20

Carrier gas name He

Flow 1 30

Flow 2 0

Number of Mix line 0

MFC Total flow 30

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Figure A.1 NH3-TPD of HZSM-5

APPENDIX A.5: Test method: ASTM D 3278-96(R11) (Flash point Analysis)

Table A.5

Flash point Analysis

Initial hydrogen pressure (bar) 20 30 40

Kerosene Flash point (deg. C)

60 75 54

Diesel 120 120 99

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APPENDIX B

RAW DATA OF EXPERIMENTSL RESULTS

Table B.1

Experimental conditions

Sample Reaction temperature

(˚C) Initial pressure (bar) Reaction time (h)

A-1 400 20 1

A-2 400 30 1

A-3 400 40 1

B-1 350 40 1

B-2 375 40 1

B-3 or A-

3 400 40 1

C-1 or A-

3 400 40 1

C-2 400 40 2

C-3 400 40 3

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Table B.2

Effect of hydrogen pressure on product yield, selectivity and conversion of waste virgin

coconut oil cracking to biofuels through hydrocracking process over HZSM-5 as

catalyst at 400 ˚C and 1 h.

Sample Material Weight (g) Yield (wt%) Selectivity (wt%) Xl (wt%)

A-1

Feed 90.75

63.9

Gasoline 1.232 1.36 1.61

Kerosene 17.280 19.04 22.59

Diesel 39.480 43.5 51.60

Residue 18.513 20.4 24.20

A-2

Feed 90.75

64.25

Gasoline 1.540 1.7 2.02

Kerosene 17.920 19.75 23.55

Diesel 39.200 42.81 51.05

Residue 17.787 19.6 23.37

A-3

Feed 90.75

66.54

Gasoline 2.464 2.72 3.23

Kerosene 19.840 21.86 26.04

Diesel 38.080 41.96 49.99

Residue 15.792 17.4 20.73

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Table B.3

Effect of temperature on product yield, selectivity and conversion of waste virgin

coconut oil cracking to biofuels through hydrocracking process over HZSM-5 as

catalyst at 40 bar and 1 h.

Sample Material Weight (g) Yield (wt%) Selectivity (wt%) Xl

(wt%)

B-1

Feed 90.75

69.55

Gasoline 0.318 0.35 0.43

Kerosene 9.600 10.58 13

Diesel 53.200 58.62 72.06

Residue 10.709 11.8 14.51

B-2

Feed 90.75

67.13

Gasoline 0.520 0.57 0.69

Kerosene 12.800 14.11 17.05

Diesel 47.600 52.45 63.40

Residue 14.157 15.6 18.86

A-3

Feed 90.75

66.54

Gasoline 2.464 2.72 3.23

Kerosene 19.840 21.86 26.04

Diesel 38.080 41.96 49.99

Residue 15.792 17.4 20.73

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Table B.4

Effect of reaction time on product yield, selectivity and conversion of waste virgin

coconut oil cracking to biofuels through hydrocracking process over HZSM-5 as

catalyst at 400 ˚C and 40 bar.

Sample Material Weight (g) Yield (wt%) Selectivity (wt%) Xl

(wt%)

A-3

Feed 90.75

66.54

Gasoline 2.464 2.72 3.23

Kerosene 19.840 21.86 26.04

Diesel 38.080 41.96 49.99

Residue 15.792 17.4 20.73

C-2

Feed 90.75

65.64

Gasoline 2.772 3.05 3.63

Kerosene 17.600 19.39 23.08

Diesel 39.200 43.2 51.40

Residue 15.7922 18.4 21.89

C-3

Feed 90.75

65.94

Gasoline 6.160 6.79 7.86

Kerosene 28.480 31.38 36.35

Diesel 25.200 27.77 32.16

Residue 18.513 20.4 23.63

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APPENDIX C

CALCULATION

%Yield, selectivity and conversion of liquid biofuel product

Example: Calculated yield, selectivity, and conversion of waste virgin coconut oil

cracking to biofuels through hydrocracking process over HZSM-5 as catalyst

(Conditions: 400˚C, 40 bar, 1 h)

Material Weight (g) Yield (wt%) Selectivity (wt%) Xl (wt%)

Feed 90.75

66.54

Gasoline 2.464 2.72 3.23

Kerosene 19.840 21.86 26.04

Diesel 38.080 41.96 49.99

Residue 15.792 17.4 20.73

𝐶𝑜𝑛𝑣𝑒𝑟𝑠𝑖𝑜𝑛 𝑜𝑓 𝑙𝑖𝑞𝑢𝑖𝑑 𝑏𝑖𝑜𝑓𝑢𝑒𝑙 𝑝𝑟𝑜𝑑𝑢𝑐𝑡 (%) = 𝑙𝑖𝑞𝑢𝑖𝑑 𝑏𝑖𝑜𝑓𝑢𝑒𝑙 𝑝𝑟𝑜𝑑𝑢𝑐𝑡 (𝑔)

𝑖𝑛𝑖𝑡𝑖𝑎𝑙 𝑓𝑒𝑒𝑑𝑠𝑡𝑜𝑐𝑘 (𝑔)𝑥 100%

= [(2.464+19.840+38.080)/90.750] x 100

= 66.54 wt%

𝑌𝑖𝑒𝑙𝑑 𝑜𝑓 𝑑𝑖𝑒𝑠𝑒𝑙 (𝑤𝑡%) = 𝑤𝑒𝑖𝑔ℎ𝑡 𝑜𝑓 𝑓𝑟𝑎𝑐𝑡𝑖𝑜𝑛𝑎𝑙 𝑑𝑖𝑠𝑡𝑖𝑙𝑙𝑎𝑡𝑖𝑜𝑛 𝑜𝑓 𝑙𝑖𝑞𝑢𝑖𝑑 𝑝𝑟𝑜𝑑𝑢𝑐𝑡 (𝑔)

𝑖𝑛𝑖𝑡𝑖𝑎𝑙 𝑓𝑒𝑒𝑑𝑠𝑡𝑜𝑐𝑘 (𝑔)𝑥 100%

= (38.080 /90.750) x 100

= 41.96 wt%

𝑆𝑒𝑙𝑒𝑐𝑡𝑖𝑣𝑖𝑡𝑦 𝑜𝑓 𝑑𝑖𝑒𝑠𝑒𝑙 (𝑤𝑡%) = 𝑤𝑒𝑖𝑔ℎ𝑡 𝑜𝑓 𝑡𝑎𝑟𝑔𝑒𝑡 𝑝𝑟𝑜𝑑𝑢𝑐𝑡 (𝑔)

𝑤𝑒𝑖𝑔ℎ𝑡 𝑜𝑓 𝑙𝑖𝑞𝑢𝑖𝑑 𝑝𝑟𝑜𝑑𝑢𝑐𝑡 (𝑔)𝑥 100%

= [38.080 / (2.464+19.840+38.080+15.792)] x 100

= 49.99 wt%

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APPENDIX D

PEARSON’S CORRELATION

Table D.1

Pearson’s correlation for operating parameters on gasoline production

Table D.2

Pearson’s correlation for operating parameters on kerosene production

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Table D.3

Pearson’s correlation for operating parameters on diesel production

Table D.4

Liquid biofuel yield comparison between experimental (actual) and model

predicted results

No.

Temperature Pressure Time Actual Predicted Actual Predicted Actual Predicted

(°C) (bar) (h) Yield of gasoline

(wt%)

Yield of kerosene

(wt%)

Yield of diesel

(wt%)

1 350 40 1 0.35 0.11 10.58 10.22 58.62 58.96

2 375 40 1 0.57 1.03 14.11 14.78 52.45 51.79

3 400 40 1 2.72 1.96 21.86 19.33 41.96 44.61

4 400 20 1 1.36 1.37 19.04 19.25 43.5 43.01

5 400 30 1 1.7 1.66 19.75 19.29 42.81 43.81

6 400 40 2 3.06 4.11 19.39 24.15 43.2 37.6

7 400 40 3 6.79 6.25 31.38 28.97 27.77 30.59

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APPENDIX E

PRODUCT DISTRIBUTION (BATCH REACTOR)

APPENDIX E.1: The product distribution was detected by gas-chromatography (batch

reactor)

Table E.1

The effect of initial hydrogen pressure on the product distribution and degree of

deoxygenation and degree of cracking

Sample

Hydrocarbon products Oxygenated

products Total

oxy DOD DOC

Gasoline Kerosene Diesel >C18 Trig.

acid.

Frag.

acid R-O

20 bar 0.09 4.90 6.18 0.00 87.43 0.07 1.30 88.80 11.20 12.50

30 bar 0.21 5.58 4.96 0.41 87.36 0.00 1.05 88.41 11.59 12.64

40 bar 0.14 5.86 5.53 0.00 86.36 0.06 1.60 88.01 11.99 13.59

*Trig. = triglyceride acid, Frag. = fragment acid

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Table E.2

The effect of reaction temperature on the product distribution and degree of

deoxygenation and degree of cracking

Sample

Hydrocarbon products Oxygenated

products Total

oxy DOD DOC

Gasoline Kerosene Diesel >C18 Trig.

acid.

Frag.

acid R-O

350 °C 0.59 0.00 3.56 0.19 94.32 0.50 0.00 94.82 5.18 5.18

375 °C 0.09 4.34 3.16 0.00 91.22 0.03 0.62 91.87 8.13 8.75

400 °C 0.14 5.86 5.53 0.00 86.36 0.06 1.60 88.01 11.99 13.59

*Trig. = triglyceride acid, Frag. = fragment acid

Table E.3

The effect of reaction time on the product distribution and degree of deoxygenation

and degree of cracking

Sample

Hydrocarbon products Oxygenated

products Total

oxy DOD DOC

Gasoline Kerosene Diesel >C18 Trig.

acid

Frag.

acid R-O

60

minutes 0.14 5.86 5.53 0.00 86.36 0.06 1.60 88.01 11.99 13.59

120

minutes 1.62 0.19 6.52 0.63 87.84 0.00 2.10 89.94 10.06 12.16

180

minutes 0.37 14.82 14.43 0.52 66.24 0.18 2.42 68.84 31.16 33.58

*Trig. = triglyceride acid, Frag. = fragment acid

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Table E.4

The product distribution and degree of deoxygenation and degree of cracking at the

condition no add catalyst (400 °C/40 bar/60 minutes) and no add hydrogen gas (400

°C/60 minutes)

Sample

Hydrocarbon products Oxygenated

products Total

oxy DOD DOC

Gasoline Kerosene Diesel >C18 Trig.

acid

Frag.

acid R-O

no cat. 0.18 0.00 0.11 0.29 98.68 0.00 0.14 98.82 1.18 1.32

no H2 0.45 0.00 0.45 0.00 97.49 0.90 0.15 98.54 1.46 1.61

*Trig. = triglyceride acid, Frag. = fragment acid

APPENDIX E.2: The calculation for the degree of deoxygenation and the degree of

cracking (batch reactor)

Example: Calculated the degree of deoxygenation and the degree of cracking of waste

virgin coconut oil cracking to biofuels through hydrocracking process over

HZSM-5 as catalyst (Conditions: 400˚C, 40 bar, 3 h)

Sample

Hydrocarbon products Oxygenated

products Total

oxy DOD DOC

Gasoline Kerosene Diesel >C18 Trig.

acid

Frag.

acid R-O

180

minute 0.37 14.82 14.43 0.52 66.24 0.18 2.42 68.84 31.16 33.58

*Trig. = triglyceride acid, Frag. = fragment acid

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𝑫𝒆𝒈𝒓𝒆𝒆 𝒐𝒇 𝒅𝒆𝒐𝒙𝒚𝒈𝒆𝒏𝒂𝒕𝒊𝒐𝒏 (𝑫𝑶𝑫) = (1 −𝑂𝑥𝑦𝑔𝑒𝑛𝑎𝑡𝑒𝑑𝑝𝑟𝑜𝑑𝑢𝑐𝑡

𝑂𝑥𝑦𝑔𝑒𝑛𝑎𝑡𝑒𝑑𝑓𝑒𝑒𝑑

) ∗ 100

= (1-68.84/100)*100

= 31.16 %

𝑫𝒆𝒈𝒓𝒆𝒆 𝒐𝒇 𝒄𝒓𝒂𝒄𝒌𝒊𝒏𝒈 (𝑫𝑶𝑪) = (1 −𝑐𝑎𝑟𝑏𝑜𝑥𝑦𝑙𝑖𝑐 𝑎𝑐𝑖𝑑𝑝𝑟𝑜𝑑𝑢𝑐𝑡

𝑐𝑎𝑟𝑏𝑜𝑥𝑦𝑙𝑖𝑐 𝑎𝑐𝑖𝑑𝑓𝑒𝑒𝑑) ∗ 100

= [1-(66.24+0.18)/100]*100

= 33.58 %

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APPENDIX E.3: Selectivity of product distribution

Table E.5

The selectivity of carbon atom number of liquid yield from hydrocracking process over

HZSM-5 were detected by gas-chromatography

Carbon

number

350

°C

375

°C

400

°C

20

bar

30

bar

40

bar

60

min

120

min

180

min

C7 13.51 1.13 1.22 0.76 1.89 1.22 1.22 18.10 0.34

C8 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.89

C9 0.00 5.28 4.50 2.04 0.00 4.50 4.50 0.00 4.95

C10 0.00 11.14 7.22 4.86 4.60 7.22 7.22 0.00 7.33

C11 0.00 33.39 32.40 31.44 37.55 32.40 32.40 0.00 29.27

C12 0.00 7.39 6.68 5.57 7.84 6.68 6.68 2.17 7.62

C13 38.13 17.66 17.17 16.57 19.16 17.17 17.17 26.31 16.29

C14 0.00 1.62 4.20 2.84 2.68 4.20 4.20 0.00 7.29

C15 27.89 11.78 20.98 14.23 14.19 20.98 20.98 27.72 12.83

C16 0.00 0.71 0.00 6.18 0.00 0.00 0.00 0.00 1.61

C17 13.34 7.92 5.21 14.18 8.45 5.21 5.21 11.85 5.96

C18 2.77 1.99 0.42 1.33 0.00 0.42 0.42 6.81 3.89

C19 0.00 0.00 0.00 0.00 3.64 0.00 0.00 0.00 0.00

C20 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

C21 0.00 0.00 0.00 0.00 0.00 0.00 0.00 7.04 1.72

C22 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

C23 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

C24 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

C25 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

C26 4.36 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00

Sum 100 100 100 100 100 100 100 100 100

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Table E.6

The distribution of aromatic, alkane, and alkene for kerosene fraction

Kerosene

fraction

350

°C

375

°C

400

°C

20

bar

30

bar

40

bar

60

min

120

min

180

min

Selectivity (%) Selectivity (%) Selectivity (%)

Aromatic 0.00 13.58 1.21 9.32 11.53 1.21 1.21 0.00 12.12

Alkane 0.00 15.75 16.80 15.57 12.55 16.80 16.80 0.00 8.57

Alkene 0.00 70.66 81.99 75.11 75.91 81.99 81.99 100.00 79.31

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APPENDIX F

PRODUCT DISTRIBUTION (CONTINUOUS PROCESS)

The product distribution was detected by gas-chromatography (continuous process)

Table F

The effect of hydrogen flow rate (ml/min) on the selectivity to product at the various

of the reaction time (°C)

Hydrogen

flow rate

(ml/min)

Reaction time (minute)

30 minutes 60 minutes 120 minutes

G K D G K D G K D

20 58.60 41.40 0.00 0.00 98.63 1.37 6.42 56.74 36.84

30 7.28 92.05 0.68 0.00 100.00 0.00 0.00 100.00 0.00

40 0.00 81.98 18.02 0.00 59.64 40.36 0.00 100.00 0.00

50 75.78 7.10 17.12 0.00 95.64 4.36 0.00 100.00 0.00

G = gasoline K =kerosene D = Diesel

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APPENDIX G

THE PROPOSED PATHWAY OF HYDROPROCESSING PROCESS (BATCH PROCESS)

Solid circles represent liquid compounds detected by GC-MS.

Dashed circles represent possible products containing in gas-phase samples which

was not collected.

Figure A.2 The proposed pathway reaction of hydroprocessing of tetradecanoic acid

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Solid circles represent liquid compounds detected by GC-MS.

Dashed circles represent possible products containing in gas-phase samples which

was not collected.

Figure A.3 The proposed pathway reaction of hydroprocessing of dodecanoic acid

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Solid circles represent liquid compounds detected by GC-MS.

Dashed circles represent possible products containing in gas-phase samples which

was not collected.

Figure A.4 The proposed pathway reaction of hydroprocessing of decanoic acid

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Solid circles represent liquid compounds detected by GC-MS.

Dashed circles represent possible products containing in gas-phase samples which

was not collected.

Figure A.5 The proposed pathway reaction of hydroprocessing of octanoic acid

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BIOGRAPHY

Name Miss Panadda Yotsomnuk

Date of Birth February 2, 1993

Educational Attainment 2015: B. Eng. (Chemical Engineering)

Silpakorn University

Scholarship Year 2015: Scholarship Thammasat University

Research Fund

Publication

Yotsomnuk, P., & Skolpap, W. (2017). Biofuel production from waste virgin coconut oil

by hydrocracking over HZSM-5 zeolite. World research library, Taipei, Taiwan,

26-27 March, 1-4. Academics World International Conference.

Ref. code: 25605810030592YLH