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STUDY ON THE POTENTIAL OF UTILIZING RICE HUSK AS BIOSORBENT FOR HUMIC SUBSTANCE
Sharifah Nurul Fazilla Binti Ghazali
QD Bachelor of Engineering with Honours
341 (Chemical Engineering) A2 2013 S531 2013
P KHIDIIAT IIAKLUIIAT AKADEIIIK
111111111111111111111111 1000268853UNIV tAWAK
Grade ____~
Please tick (1) Final Year Project Report [] ~asters c===J PhD D
DECLARATION OF ORIGINAL WORK
This declaration is made on theltday ofM~y2013
Students Declaration
I SHAIUfAH NJJRlJkfAU~LA ~JNTJ QHAZA~J (~1~~m JJEPT Of QREMJCM ENQINEERlNG ANP ENERGY SJ$TAlNNUMTYL fAQ1JLTY Of ENQJNEEJUNG hereby declare that the work entitled STlJDYoNTHE rQTENTlALOf1JTJLIZJNGRI~E RJ$KAS uSOR~ENTfQRRJMI~Sm~$TAN~Eis my original work I have not copied from any other students work or from any other sources except where due to reference or acknowledgement is made explicitly in the text nor has any part been written for me by another person
JQMAY~QJ3 $lJAlnfMJNlJRJLfAZI1LAG~4~~~) Date submitted Name of the student (Matric No)
Supervisors Declaration
I MOJJP fARlP ATAN hereby certifies that the work entitledST1JPY ON TBE PQTENTIAL QfJJTILJZJNG mCEJJlJSKNtmSQR~ENTFORHJJMIgSJJ~$TAN~E was prepared by the above named student and was submitted to the FACULTY as a partial fulfillment for the conferment of ~AgHELQRof ENGINEERING wnH RONQ1JRS (gHEMI~AJENmNEERJNQ)~ and the aforementioned work to the best of my knowledge is the said students work
Received for examination by MoHP fARlPATAN Date HLMAY~QJ3 (Name of the supervisor)
I declare this ProjectThesis is classified as (Please tick (-J)
~ CONFIDENTIAL (Contains confidential information under the Official Secret Act 1972)
o RESTRICTED (Contains restricted information as specified by the organisation where research was done)
o OPEN ACCESS
Validation of Projectffhesis
I therefore duly affirmed with free consent and willingness declare that this said ProjectlThesis shall be placed officially in the Centre for Academic Information Services with the abiding interest and rights as follows
bull This ProjectlThesis is the sole legal property of Universiti Malaysia Sarawak (UNIMAS)
bull The Centre for Academic Information Services has the lawful right to make copies for the purpose of academic and research only and not for other purpose
bull The Centre for Academic Information Services has the lawful right to digitalise the content for the Local Content Database
bull The Centre for Academic Information Services has the lawful right to make copies of the ProjectlThesis for academic exchange between Higher Learning Institute
bull No dispute or any claim shall arise from the student itself neither third party on this ProjectThesis once it becomes the sole property of UNIMAS
bull This ProjectlThesis or any material data and information related to it shall not be distributed published or disclosed to any party by the student except with UNIMAS permission
L~ D Students signature ___~-+ ____ Supervisors signature 1~~_
(1~Y2013) dtrMAY 2( 13)
Current Address
K~HPiluimnIJIJt~CIJy~sectI(i6J99IJIJt~CIJy~sectI~~JIJm~Q~DIJXyJ~hIHL
Notes If the ProjectlThesis is CONFIDENTIAL or RESTRICTED please attach together as annexure a letter from the organisation with the period and reasons of confidentiality and restriction
[The instrument is duly prepared by The Centre for Academic Information Services)
11
APPROVAL SHEET
This final year report which entitled Study on the Potential of Utilizing Rice Husk
as Biorsorbent for Humic Substance was prepared by Sharifah Nurul Fazilla
Ghazali (24996) as a partial fulfilment for the Degree of Bachelor of Chemical
Engineering is hereby read and approved by
(Supervisor)
III
UNlMAS
10 Mei 2013
Pustakawan
Pusat Khidmat Maklumat Akademik
Universiti Malaysia Sarawak
Puan
Laporan Projek Tahun Akhir
Laporan pelajar ini adalah dikategorikan sebagai terhad selama 2 tahun Hal
ini kerana maklumat yang terkandung adalah berkaitan dengan geran
pendidikan yang masih berjalan
Sekian Terima Kasih
Yang benar
En Mohd Farid Atan
Penyelia Projek
Kejuruteraan Kimia amp Sustainabiliti Tenaga
Fakulti Kejuruteraan
IV
Pusat Khidmat Maklumat Akademh UNlVERSm MALAYSIA SARAWAJ(
STUDY ON THE POTENTIAL OF UTILIZING RICE HUSK AS
BIOSORBENT FOR HUMIC SUBSTANCE
SHARIFAH NURUL FAZILLA BINTI GHAZALI
Thesis is submitted to
Faculty of Engineering Universiti Malaysia Sarawak
In Partial Fulfilment of the Requirements
For the Degree of Bachelor of Engineering
Chemical Engineering (With Honours)
2013
v
I
I
Dedicated to my beloved dad and mom supervisor lecturers and friends
who always bestow me sustainable motivations inspirations and
encouragements
VI
ACKNOWLEDGEMENT
The author would like to express her sincerest appreciation to
supportive and helpful supervisor Mr Mohd Farid Atan for guidance
supports and valuables knowledge as well as for invaluable supervision
towards the completion of this research project The author also takes this
opportunity to express her gratitude to Co-Supervisor Mr Nazeri Abdul
Rahman and Dr Shanti Faridah Salleh for their willingness to give the
ideas and moral support along the implementation of the project Special
thanks are dedicated to authors family who always give her supports and
love Last but not least the authors would like to express her pleasure to
all of the staff from Department of Chemical Engineering amp Energy
Sustainability friends and all individuals that have contributed and
cooperated throughout in completing this project
Vll
ABSTRAK Pada masa kini pengguna mengambil berat tentang kualiti aIr yang
dibekalkan untuk memastikan ianya bebas daripada bahan berbahaya seperti
Bahan humik Bahan Humik mengandungi tiga (3) komponen utama iaitu Asid
Humik Asid Fulvik dan Humin Asid Humik berkepekatan tinggi di dalam air
minuman boleh menyebabkan penyakit kepada manusia seperti kanser perut
Justeru ia adalah penting untuk mengenalpasti satu kaedah baru untuk
meningkatkan kualiti air minuman Kaedah penjerapan adalah cara yang
terbaik yang dapat digunakan untuk memjerap Bahan Humik Berdasarkan
daripada hasil penyelidikan yang dijalankan sebelum ini Activated Carbon
digunakan untuk membuang Bahan Humik tetapi ianya menelan kos yang agak
tinggi Oleh itu sekam padi adalah penjerap terbaik di dalam merawat sisa
kumbahan berbanding dengan sisa pertanian yang lain Hal ini kerana struktur
dan sifat-sifat sekam padi sebagai penjerap Pemanasan dan pengubahsuaian
sekam padi dengan menggunakan Poly (Acrylamide) Carboxyl Modified dan
Potassium Carbonate mempunyai kesan signifikasi ke atas penjerapan Bahan
Humik Keputusan eksperimen menunjukkan kadar penjerapan yang tinggi
diperolehi dengan mencuci sekam padi dengan Poly (Acrylamide) Carboxyl
Modified kerana Peratusan Transmitansi () daripada kumpulan berfungsi
Karboksilik serta kumpulan Amine berkurangan Sebaliknya untuk kumpulan
Aromatik sekam padi yang tidak dirawat adalah penjerap cara terbaik untuk
penjerapan dalam Bahan Humik
Kata Kunci Bahan Humik Asid Humik Penjerapan Sekam Padi Penjerap Poly
(Acrylamide) Carboxyl Modified Potassium Carbonate
Vlll
ABSTRACT
Nowadays consumers concern about the quality of water that being
supplied in order to ensure the water supplied is free from any harmful
substances like Humic Substances (HS) HS are divided into three main fractions
which are Humic Acid Fulvic Acid and Humin High concentration of Humic
Acid in drinking water can cause disease for human like stomach cancer Thus it
is important to develop a new technique to improve the quality of drinking water
Therefore adsorption method is the best way that can be used in order to remove
HS Moreover from the previous research activated carbon has been used to
remove HS but it is costly As an alternative way Rice husk has been used as an
adsorbent in the wastewater treatment compared to other agricultural waste due
to its structure and characteristics as adsorbent Heating and utilization of
chemical modifier like Poly (Acrylamide) Carboxyl Modified and Potassium
Carbonate can have a significant impact on adsorption of HS The result has
shown that rice husk which is treated with Poly (Acrylamide) Carboxyl Modified
occurs the highest rate of adsorption of HS because the Percentage of
Transmittance () of Carboxylic functional groups decreases as well as the
presence of Amine groups in the wastewater However for Aromatic groups
untreated rice husk become the best adsorbent for HS
Keyword Humic Substances Humic Acid Adsorption Rice Hush Adsorbent Poly
(Aery lam ide) Carboxyl Modified Potassium Carbonate
IX
iusat Khid a Mak1umat Akadtmil UNlVERSm MALAYSIA SARAWAJ(
TABLE OF CONTENTS
Pages
DECLARATION OF ORIGINAL WORK
APPROVAL SHEET III
ACKNOWLEDGEMENT Vll
ABSTRAK VllI
ABSTRACT LX
LIST OF TABLES XUI
NOMENCLATURE XVIll
APPROVAL CONFIDENTIAL LETTER IV
TITLE PAGE V
DEDICATION VI
TABLE OF CONTENTS x
LIST OF FIGURES XIV
ABBREVIATIONS XVI
CHAPTER 1 INTRODUCTION
11 General 1
111 Humic Substances 1
112 Main Component of Humic Substance 2
113 Effect on Humic Substances 3
114 Method of Filtrations of Humic Substance 3
115 Adsorption 4
116 Potential of Agricultural Waste in Malaysia 4
Type of Agricultural Waste 6
12 Problem Statements 8
13 Objectives 9
14 Methodology 10
15 Expected Outcome 12
X
shy---=-shy-
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
P KHIDIIAT IIAKLUIIAT AKADEIIIK
111111111111111111111111 1000268853UNIV tAWAK
Grade ____~
Please tick (1) Final Year Project Report [] ~asters c===J PhD D
DECLARATION OF ORIGINAL WORK
This declaration is made on theltday ofM~y2013
Students Declaration
I SHAIUfAH NJJRlJkfAU~LA ~JNTJ QHAZA~J (~1~~m JJEPT Of QREMJCM ENQINEERlNG ANP ENERGY SJ$TAlNNUMTYL fAQ1JLTY Of ENQJNEEJUNG hereby declare that the work entitled STlJDYoNTHE rQTENTlALOf1JTJLIZJNGRI~E RJ$KAS uSOR~ENTfQRRJMI~Sm~$TAN~Eis my original work I have not copied from any other students work or from any other sources except where due to reference or acknowledgement is made explicitly in the text nor has any part been written for me by another person
JQMAY~QJ3 $lJAlnfMJNlJRJLfAZI1LAG~4~~~) Date submitted Name of the student (Matric No)
Supervisors Declaration
I MOJJP fARlP ATAN hereby certifies that the work entitledST1JPY ON TBE PQTENTIAL QfJJTILJZJNG mCEJJlJSKNtmSQR~ENTFORHJJMIgSJJ~$TAN~E was prepared by the above named student and was submitted to the FACULTY as a partial fulfillment for the conferment of ~AgHELQRof ENGINEERING wnH RONQ1JRS (gHEMI~AJENmNEERJNQ)~ and the aforementioned work to the best of my knowledge is the said students work
Received for examination by MoHP fARlPATAN Date HLMAY~QJ3 (Name of the supervisor)
I declare this ProjectThesis is classified as (Please tick (-J)
~ CONFIDENTIAL (Contains confidential information under the Official Secret Act 1972)
o RESTRICTED (Contains restricted information as specified by the organisation where research was done)
o OPEN ACCESS
Validation of Projectffhesis
I therefore duly affirmed with free consent and willingness declare that this said ProjectlThesis shall be placed officially in the Centre for Academic Information Services with the abiding interest and rights as follows
bull This ProjectlThesis is the sole legal property of Universiti Malaysia Sarawak (UNIMAS)
bull The Centre for Academic Information Services has the lawful right to make copies for the purpose of academic and research only and not for other purpose
bull The Centre for Academic Information Services has the lawful right to digitalise the content for the Local Content Database
bull The Centre for Academic Information Services has the lawful right to make copies of the ProjectlThesis for academic exchange between Higher Learning Institute
bull No dispute or any claim shall arise from the student itself neither third party on this ProjectThesis once it becomes the sole property of UNIMAS
bull This ProjectlThesis or any material data and information related to it shall not be distributed published or disclosed to any party by the student except with UNIMAS permission
L~ D Students signature ___~-+ ____ Supervisors signature 1~~_
(1~Y2013) dtrMAY 2( 13)
Current Address
K~HPiluimnIJIJt~CIJy~sectI(i6J99IJIJt~CIJy~sectI~~JIJm~Q~DIJXyJ~hIHL
Notes If the ProjectlThesis is CONFIDENTIAL or RESTRICTED please attach together as annexure a letter from the organisation with the period and reasons of confidentiality and restriction
[The instrument is duly prepared by The Centre for Academic Information Services)
11
APPROVAL SHEET
This final year report which entitled Study on the Potential of Utilizing Rice Husk
as Biorsorbent for Humic Substance was prepared by Sharifah Nurul Fazilla
Ghazali (24996) as a partial fulfilment for the Degree of Bachelor of Chemical
Engineering is hereby read and approved by
(Supervisor)
III
UNlMAS
10 Mei 2013
Pustakawan
Pusat Khidmat Maklumat Akademik
Universiti Malaysia Sarawak
Puan
Laporan Projek Tahun Akhir
Laporan pelajar ini adalah dikategorikan sebagai terhad selama 2 tahun Hal
ini kerana maklumat yang terkandung adalah berkaitan dengan geran
pendidikan yang masih berjalan
Sekian Terima Kasih
Yang benar
En Mohd Farid Atan
Penyelia Projek
Kejuruteraan Kimia amp Sustainabiliti Tenaga
Fakulti Kejuruteraan
IV
Pusat Khidmat Maklumat Akademh UNlVERSm MALAYSIA SARAWAJ(
STUDY ON THE POTENTIAL OF UTILIZING RICE HUSK AS
BIOSORBENT FOR HUMIC SUBSTANCE
SHARIFAH NURUL FAZILLA BINTI GHAZALI
Thesis is submitted to
Faculty of Engineering Universiti Malaysia Sarawak
In Partial Fulfilment of the Requirements
For the Degree of Bachelor of Engineering
Chemical Engineering (With Honours)
2013
v
I
I
Dedicated to my beloved dad and mom supervisor lecturers and friends
who always bestow me sustainable motivations inspirations and
encouragements
VI
ACKNOWLEDGEMENT
The author would like to express her sincerest appreciation to
supportive and helpful supervisor Mr Mohd Farid Atan for guidance
supports and valuables knowledge as well as for invaluable supervision
towards the completion of this research project The author also takes this
opportunity to express her gratitude to Co-Supervisor Mr Nazeri Abdul
Rahman and Dr Shanti Faridah Salleh for their willingness to give the
ideas and moral support along the implementation of the project Special
thanks are dedicated to authors family who always give her supports and
love Last but not least the authors would like to express her pleasure to
all of the staff from Department of Chemical Engineering amp Energy
Sustainability friends and all individuals that have contributed and
cooperated throughout in completing this project
Vll
ABSTRAK Pada masa kini pengguna mengambil berat tentang kualiti aIr yang
dibekalkan untuk memastikan ianya bebas daripada bahan berbahaya seperti
Bahan humik Bahan Humik mengandungi tiga (3) komponen utama iaitu Asid
Humik Asid Fulvik dan Humin Asid Humik berkepekatan tinggi di dalam air
minuman boleh menyebabkan penyakit kepada manusia seperti kanser perut
Justeru ia adalah penting untuk mengenalpasti satu kaedah baru untuk
meningkatkan kualiti air minuman Kaedah penjerapan adalah cara yang
terbaik yang dapat digunakan untuk memjerap Bahan Humik Berdasarkan
daripada hasil penyelidikan yang dijalankan sebelum ini Activated Carbon
digunakan untuk membuang Bahan Humik tetapi ianya menelan kos yang agak
tinggi Oleh itu sekam padi adalah penjerap terbaik di dalam merawat sisa
kumbahan berbanding dengan sisa pertanian yang lain Hal ini kerana struktur
dan sifat-sifat sekam padi sebagai penjerap Pemanasan dan pengubahsuaian
sekam padi dengan menggunakan Poly (Acrylamide) Carboxyl Modified dan
Potassium Carbonate mempunyai kesan signifikasi ke atas penjerapan Bahan
Humik Keputusan eksperimen menunjukkan kadar penjerapan yang tinggi
diperolehi dengan mencuci sekam padi dengan Poly (Acrylamide) Carboxyl
Modified kerana Peratusan Transmitansi () daripada kumpulan berfungsi
Karboksilik serta kumpulan Amine berkurangan Sebaliknya untuk kumpulan
Aromatik sekam padi yang tidak dirawat adalah penjerap cara terbaik untuk
penjerapan dalam Bahan Humik
Kata Kunci Bahan Humik Asid Humik Penjerapan Sekam Padi Penjerap Poly
(Acrylamide) Carboxyl Modified Potassium Carbonate
Vlll
ABSTRACT
Nowadays consumers concern about the quality of water that being
supplied in order to ensure the water supplied is free from any harmful
substances like Humic Substances (HS) HS are divided into three main fractions
which are Humic Acid Fulvic Acid and Humin High concentration of Humic
Acid in drinking water can cause disease for human like stomach cancer Thus it
is important to develop a new technique to improve the quality of drinking water
Therefore adsorption method is the best way that can be used in order to remove
HS Moreover from the previous research activated carbon has been used to
remove HS but it is costly As an alternative way Rice husk has been used as an
adsorbent in the wastewater treatment compared to other agricultural waste due
to its structure and characteristics as adsorbent Heating and utilization of
chemical modifier like Poly (Acrylamide) Carboxyl Modified and Potassium
Carbonate can have a significant impact on adsorption of HS The result has
shown that rice husk which is treated with Poly (Acrylamide) Carboxyl Modified
occurs the highest rate of adsorption of HS because the Percentage of
Transmittance () of Carboxylic functional groups decreases as well as the
presence of Amine groups in the wastewater However for Aromatic groups
untreated rice husk become the best adsorbent for HS
Keyword Humic Substances Humic Acid Adsorption Rice Hush Adsorbent Poly
(Aery lam ide) Carboxyl Modified Potassium Carbonate
IX
iusat Khid a Mak1umat Akadtmil UNlVERSm MALAYSIA SARAWAJ(
TABLE OF CONTENTS
Pages
DECLARATION OF ORIGINAL WORK
APPROVAL SHEET III
ACKNOWLEDGEMENT Vll
ABSTRAK VllI
ABSTRACT LX
LIST OF TABLES XUI
NOMENCLATURE XVIll
APPROVAL CONFIDENTIAL LETTER IV
TITLE PAGE V
DEDICATION VI
TABLE OF CONTENTS x
LIST OF FIGURES XIV
ABBREVIATIONS XVI
CHAPTER 1 INTRODUCTION
11 General 1
111 Humic Substances 1
112 Main Component of Humic Substance 2
113 Effect on Humic Substances 3
114 Method of Filtrations of Humic Substance 3
115 Adsorption 4
116 Potential of Agricultural Waste in Malaysia 4
Type of Agricultural Waste 6
12 Problem Statements 8
13 Objectives 9
14 Methodology 10
15 Expected Outcome 12
X
shy---=-shy-
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
I declare this ProjectThesis is classified as (Please tick (-J)
~ CONFIDENTIAL (Contains confidential information under the Official Secret Act 1972)
o RESTRICTED (Contains restricted information as specified by the organisation where research was done)
o OPEN ACCESS
Validation of Projectffhesis
I therefore duly affirmed with free consent and willingness declare that this said ProjectlThesis shall be placed officially in the Centre for Academic Information Services with the abiding interest and rights as follows
bull This ProjectlThesis is the sole legal property of Universiti Malaysia Sarawak (UNIMAS)
bull The Centre for Academic Information Services has the lawful right to make copies for the purpose of academic and research only and not for other purpose
bull The Centre for Academic Information Services has the lawful right to digitalise the content for the Local Content Database
bull The Centre for Academic Information Services has the lawful right to make copies of the ProjectlThesis for academic exchange between Higher Learning Institute
bull No dispute or any claim shall arise from the student itself neither third party on this ProjectThesis once it becomes the sole property of UNIMAS
bull This ProjectlThesis or any material data and information related to it shall not be distributed published or disclosed to any party by the student except with UNIMAS permission
L~ D Students signature ___~-+ ____ Supervisors signature 1~~_
(1~Y2013) dtrMAY 2( 13)
Current Address
K~HPiluimnIJIJt~CIJy~sectI(i6J99IJIJt~CIJy~sectI~~JIJm~Q~DIJXyJ~hIHL
Notes If the ProjectlThesis is CONFIDENTIAL or RESTRICTED please attach together as annexure a letter from the organisation with the period and reasons of confidentiality and restriction
[The instrument is duly prepared by The Centre for Academic Information Services)
11
APPROVAL SHEET
This final year report which entitled Study on the Potential of Utilizing Rice Husk
as Biorsorbent for Humic Substance was prepared by Sharifah Nurul Fazilla
Ghazali (24996) as a partial fulfilment for the Degree of Bachelor of Chemical
Engineering is hereby read and approved by
(Supervisor)
III
UNlMAS
10 Mei 2013
Pustakawan
Pusat Khidmat Maklumat Akademik
Universiti Malaysia Sarawak
Puan
Laporan Projek Tahun Akhir
Laporan pelajar ini adalah dikategorikan sebagai terhad selama 2 tahun Hal
ini kerana maklumat yang terkandung adalah berkaitan dengan geran
pendidikan yang masih berjalan
Sekian Terima Kasih
Yang benar
En Mohd Farid Atan
Penyelia Projek
Kejuruteraan Kimia amp Sustainabiliti Tenaga
Fakulti Kejuruteraan
IV
Pusat Khidmat Maklumat Akademh UNlVERSm MALAYSIA SARAWAJ(
STUDY ON THE POTENTIAL OF UTILIZING RICE HUSK AS
BIOSORBENT FOR HUMIC SUBSTANCE
SHARIFAH NURUL FAZILLA BINTI GHAZALI
Thesis is submitted to
Faculty of Engineering Universiti Malaysia Sarawak
In Partial Fulfilment of the Requirements
For the Degree of Bachelor of Engineering
Chemical Engineering (With Honours)
2013
v
I
I
Dedicated to my beloved dad and mom supervisor lecturers and friends
who always bestow me sustainable motivations inspirations and
encouragements
VI
ACKNOWLEDGEMENT
The author would like to express her sincerest appreciation to
supportive and helpful supervisor Mr Mohd Farid Atan for guidance
supports and valuables knowledge as well as for invaluable supervision
towards the completion of this research project The author also takes this
opportunity to express her gratitude to Co-Supervisor Mr Nazeri Abdul
Rahman and Dr Shanti Faridah Salleh for their willingness to give the
ideas and moral support along the implementation of the project Special
thanks are dedicated to authors family who always give her supports and
love Last but not least the authors would like to express her pleasure to
all of the staff from Department of Chemical Engineering amp Energy
Sustainability friends and all individuals that have contributed and
cooperated throughout in completing this project
Vll
ABSTRAK Pada masa kini pengguna mengambil berat tentang kualiti aIr yang
dibekalkan untuk memastikan ianya bebas daripada bahan berbahaya seperti
Bahan humik Bahan Humik mengandungi tiga (3) komponen utama iaitu Asid
Humik Asid Fulvik dan Humin Asid Humik berkepekatan tinggi di dalam air
minuman boleh menyebabkan penyakit kepada manusia seperti kanser perut
Justeru ia adalah penting untuk mengenalpasti satu kaedah baru untuk
meningkatkan kualiti air minuman Kaedah penjerapan adalah cara yang
terbaik yang dapat digunakan untuk memjerap Bahan Humik Berdasarkan
daripada hasil penyelidikan yang dijalankan sebelum ini Activated Carbon
digunakan untuk membuang Bahan Humik tetapi ianya menelan kos yang agak
tinggi Oleh itu sekam padi adalah penjerap terbaik di dalam merawat sisa
kumbahan berbanding dengan sisa pertanian yang lain Hal ini kerana struktur
dan sifat-sifat sekam padi sebagai penjerap Pemanasan dan pengubahsuaian
sekam padi dengan menggunakan Poly (Acrylamide) Carboxyl Modified dan
Potassium Carbonate mempunyai kesan signifikasi ke atas penjerapan Bahan
Humik Keputusan eksperimen menunjukkan kadar penjerapan yang tinggi
diperolehi dengan mencuci sekam padi dengan Poly (Acrylamide) Carboxyl
Modified kerana Peratusan Transmitansi () daripada kumpulan berfungsi
Karboksilik serta kumpulan Amine berkurangan Sebaliknya untuk kumpulan
Aromatik sekam padi yang tidak dirawat adalah penjerap cara terbaik untuk
penjerapan dalam Bahan Humik
Kata Kunci Bahan Humik Asid Humik Penjerapan Sekam Padi Penjerap Poly
(Acrylamide) Carboxyl Modified Potassium Carbonate
Vlll
ABSTRACT
Nowadays consumers concern about the quality of water that being
supplied in order to ensure the water supplied is free from any harmful
substances like Humic Substances (HS) HS are divided into three main fractions
which are Humic Acid Fulvic Acid and Humin High concentration of Humic
Acid in drinking water can cause disease for human like stomach cancer Thus it
is important to develop a new technique to improve the quality of drinking water
Therefore adsorption method is the best way that can be used in order to remove
HS Moreover from the previous research activated carbon has been used to
remove HS but it is costly As an alternative way Rice husk has been used as an
adsorbent in the wastewater treatment compared to other agricultural waste due
to its structure and characteristics as adsorbent Heating and utilization of
chemical modifier like Poly (Acrylamide) Carboxyl Modified and Potassium
Carbonate can have a significant impact on adsorption of HS The result has
shown that rice husk which is treated with Poly (Acrylamide) Carboxyl Modified
occurs the highest rate of adsorption of HS because the Percentage of
Transmittance () of Carboxylic functional groups decreases as well as the
presence of Amine groups in the wastewater However for Aromatic groups
untreated rice husk become the best adsorbent for HS
Keyword Humic Substances Humic Acid Adsorption Rice Hush Adsorbent Poly
(Aery lam ide) Carboxyl Modified Potassium Carbonate
IX
iusat Khid a Mak1umat Akadtmil UNlVERSm MALAYSIA SARAWAJ(
TABLE OF CONTENTS
Pages
DECLARATION OF ORIGINAL WORK
APPROVAL SHEET III
ACKNOWLEDGEMENT Vll
ABSTRAK VllI
ABSTRACT LX
LIST OF TABLES XUI
NOMENCLATURE XVIll
APPROVAL CONFIDENTIAL LETTER IV
TITLE PAGE V
DEDICATION VI
TABLE OF CONTENTS x
LIST OF FIGURES XIV
ABBREVIATIONS XVI
CHAPTER 1 INTRODUCTION
11 General 1
111 Humic Substances 1
112 Main Component of Humic Substance 2
113 Effect on Humic Substances 3
114 Method of Filtrations of Humic Substance 3
115 Adsorption 4
116 Potential of Agricultural Waste in Malaysia 4
Type of Agricultural Waste 6
12 Problem Statements 8
13 Objectives 9
14 Methodology 10
15 Expected Outcome 12
X
shy---=-shy-
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
APPROVAL SHEET
This final year report which entitled Study on the Potential of Utilizing Rice Husk
as Biorsorbent for Humic Substance was prepared by Sharifah Nurul Fazilla
Ghazali (24996) as a partial fulfilment for the Degree of Bachelor of Chemical
Engineering is hereby read and approved by
(Supervisor)
III
UNlMAS
10 Mei 2013
Pustakawan
Pusat Khidmat Maklumat Akademik
Universiti Malaysia Sarawak
Puan
Laporan Projek Tahun Akhir
Laporan pelajar ini adalah dikategorikan sebagai terhad selama 2 tahun Hal
ini kerana maklumat yang terkandung adalah berkaitan dengan geran
pendidikan yang masih berjalan
Sekian Terima Kasih
Yang benar
En Mohd Farid Atan
Penyelia Projek
Kejuruteraan Kimia amp Sustainabiliti Tenaga
Fakulti Kejuruteraan
IV
Pusat Khidmat Maklumat Akademh UNlVERSm MALAYSIA SARAWAJ(
STUDY ON THE POTENTIAL OF UTILIZING RICE HUSK AS
BIOSORBENT FOR HUMIC SUBSTANCE
SHARIFAH NURUL FAZILLA BINTI GHAZALI
Thesis is submitted to
Faculty of Engineering Universiti Malaysia Sarawak
In Partial Fulfilment of the Requirements
For the Degree of Bachelor of Engineering
Chemical Engineering (With Honours)
2013
v
I
I
Dedicated to my beloved dad and mom supervisor lecturers and friends
who always bestow me sustainable motivations inspirations and
encouragements
VI
ACKNOWLEDGEMENT
The author would like to express her sincerest appreciation to
supportive and helpful supervisor Mr Mohd Farid Atan for guidance
supports and valuables knowledge as well as for invaluable supervision
towards the completion of this research project The author also takes this
opportunity to express her gratitude to Co-Supervisor Mr Nazeri Abdul
Rahman and Dr Shanti Faridah Salleh for their willingness to give the
ideas and moral support along the implementation of the project Special
thanks are dedicated to authors family who always give her supports and
love Last but not least the authors would like to express her pleasure to
all of the staff from Department of Chemical Engineering amp Energy
Sustainability friends and all individuals that have contributed and
cooperated throughout in completing this project
Vll
ABSTRAK Pada masa kini pengguna mengambil berat tentang kualiti aIr yang
dibekalkan untuk memastikan ianya bebas daripada bahan berbahaya seperti
Bahan humik Bahan Humik mengandungi tiga (3) komponen utama iaitu Asid
Humik Asid Fulvik dan Humin Asid Humik berkepekatan tinggi di dalam air
minuman boleh menyebabkan penyakit kepada manusia seperti kanser perut
Justeru ia adalah penting untuk mengenalpasti satu kaedah baru untuk
meningkatkan kualiti air minuman Kaedah penjerapan adalah cara yang
terbaik yang dapat digunakan untuk memjerap Bahan Humik Berdasarkan
daripada hasil penyelidikan yang dijalankan sebelum ini Activated Carbon
digunakan untuk membuang Bahan Humik tetapi ianya menelan kos yang agak
tinggi Oleh itu sekam padi adalah penjerap terbaik di dalam merawat sisa
kumbahan berbanding dengan sisa pertanian yang lain Hal ini kerana struktur
dan sifat-sifat sekam padi sebagai penjerap Pemanasan dan pengubahsuaian
sekam padi dengan menggunakan Poly (Acrylamide) Carboxyl Modified dan
Potassium Carbonate mempunyai kesan signifikasi ke atas penjerapan Bahan
Humik Keputusan eksperimen menunjukkan kadar penjerapan yang tinggi
diperolehi dengan mencuci sekam padi dengan Poly (Acrylamide) Carboxyl
Modified kerana Peratusan Transmitansi () daripada kumpulan berfungsi
Karboksilik serta kumpulan Amine berkurangan Sebaliknya untuk kumpulan
Aromatik sekam padi yang tidak dirawat adalah penjerap cara terbaik untuk
penjerapan dalam Bahan Humik
Kata Kunci Bahan Humik Asid Humik Penjerapan Sekam Padi Penjerap Poly
(Acrylamide) Carboxyl Modified Potassium Carbonate
Vlll
ABSTRACT
Nowadays consumers concern about the quality of water that being
supplied in order to ensure the water supplied is free from any harmful
substances like Humic Substances (HS) HS are divided into three main fractions
which are Humic Acid Fulvic Acid and Humin High concentration of Humic
Acid in drinking water can cause disease for human like stomach cancer Thus it
is important to develop a new technique to improve the quality of drinking water
Therefore adsorption method is the best way that can be used in order to remove
HS Moreover from the previous research activated carbon has been used to
remove HS but it is costly As an alternative way Rice husk has been used as an
adsorbent in the wastewater treatment compared to other agricultural waste due
to its structure and characteristics as adsorbent Heating and utilization of
chemical modifier like Poly (Acrylamide) Carboxyl Modified and Potassium
Carbonate can have a significant impact on adsorption of HS The result has
shown that rice husk which is treated with Poly (Acrylamide) Carboxyl Modified
occurs the highest rate of adsorption of HS because the Percentage of
Transmittance () of Carboxylic functional groups decreases as well as the
presence of Amine groups in the wastewater However for Aromatic groups
untreated rice husk become the best adsorbent for HS
Keyword Humic Substances Humic Acid Adsorption Rice Hush Adsorbent Poly
(Aery lam ide) Carboxyl Modified Potassium Carbonate
IX
iusat Khid a Mak1umat Akadtmil UNlVERSm MALAYSIA SARAWAJ(
TABLE OF CONTENTS
Pages
DECLARATION OF ORIGINAL WORK
APPROVAL SHEET III
ACKNOWLEDGEMENT Vll
ABSTRAK VllI
ABSTRACT LX
LIST OF TABLES XUI
NOMENCLATURE XVIll
APPROVAL CONFIDENTIAL LETTER IV
TITLE PAGE V
DEDICATION VI
TABLE OF CONTENTS x
LIST OF FIGURES XIV
ABBREVIATIONS XVI
CHAPTER 1 INTRODUCTION
11 General 1
111 Humic Substances 1
112 Main Component of Humic Substance 2
113 Effect on Humic Substances 3
114 Method of Filtrations of Humic Substance 3
115 Adsorption 4
116 Potential of Agricultural Waste in Malaysia 4
Type of Agricultural Waste 6
12 Problem Statements 8
13 Objectives 9
14 Methodology 10
15 Expected Outcome 12
X
shy---=-shy-
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
UNlMAS
10 Mei 2013
Pustakawan
Pusat Khidmat Maklumat Akademik
Universiti Malaysia Sarawak
Puan
Laporan Projek Tahun Akhir
Laporan pelajar ini adalah dikategorikan sebagai terhad selama 2 tahun Hal
ini kerana maklumat yang terkandung adalah berkaitan dengan geran
pendidikan yang masih berjalan
Sekian Terima Kasih
Yang benar
En Mohd Farid Atan
Penyelia Projek
Kejuruteraan Kimia amp Sustainabiliti Tenaga
Fakulti Kejuruteraan
IV
Pusat Khidmat Maklumat Akademh UNlVERSm MALAYSIA SARAWAJ(
STUDY ON THE POTENTIAL OF UTILIZING RICE HUSK AS
BIOSORBENT FOR HUMIC SUBSTANCE
SHARIFAH NURUL FAZILLA BINTI GHAZALI
Thesis is submitted to
Faculty of Engineering Universiti Malaysia Sarawak
In Partial Fulfilment of the Requirements
For the Degree of Bachelor of Engineering
Chemical Engineering (With Honours)
2013
v
I
I
Dedicated to my beloved dad and mom supervisor lecturers and friends
who always bestow me sustainable motivations inspirations and
encouragements
VI
ACKNOWLEDGEMENT
The author would like to express her sincerest appreciation to
supportive and helpful supervisor Mr Mohd Farid Atan for guidance
supports and valuables knowledge as well as for invaluable supervision
towards the completion of this research project The author also takes this
opportunity to express her gratitude to Co-Supervisor Mr Nazeri Abdul
Rahman and Dr Shanti Faridah Salleh for their willingness to give the
ideas and moral support along the implementation of the project Special
thanks are dedicated to authors family who always give her supports and
love Last but not least the authors would like to express her pleasure to
all of the staff from Department of Chemical Engineering amp Energy
Sustainability friends and all individuals that have contributed and
cooperated throughout in completing this project
Vll
ABSTRAK Pada masa kini pengguna mengambil berat tentang kualiti aIr yang
dibekalkan untuk memastikan ianya bebas daripada bahan berbahaya seperti
Bahan humik Bahan Humik mengandungi tiga (3) komponen utama iaitu Asid
Humik Asid Fulvik dan Humin Asid Humik berkepekatan tinggi di dalam air
minuman boleh menyebabkan penyakit kepada manusia seperti kanser perut
Justeru ia adalah penting untuk mengenalpasti satu kaedah baru untuk
meningkatkan kualiti air minuman Kaedah penjerapan adalah cara yang
terbaik yang dapat digunakan untuk memjerap Bahan Humik Berdasarkan
daripada hasil penyelidikan yang dijalankan sebelum ini Activated Carbon
digunakan untuk membuang Bahan Humik tetapi ianya menelan kos yang agak
tinggi Oleh itu sekam padi adalah penjerap terbaik di dalam merawat sisa
kumbahan berbanding dengan sisa pertanian yang lain Hal ini kerana struktur
dan sifat-sifat sekam padi sebagai penjerap Pemanasan dan pengubahsuaian
sekam padi dengan menggunakan Poly (Acrylamide) Carboxyl Modified dan
Potassium Carbonate mempunyai kesan signifikasi ke atas penjerapan Bahan
Humik Keputusan eksperimen menunjukkan kadar penjerapan yang tinggi
diperolehi dengan mencuci sekam padi dengan Poly (Acrylamide) Carboxyl
Modified kerana Peratusan Transmitansi () daripada kumpulan berfungsi
Karboksilik serta kumpulan Amine berkurangan Sebaliknya untuk kumpulan
Aromatik sekam padi yang tidak dirawat adalah penjerap cara terbaik untuk
penjerapan dalam Bahan Humik
Kata Kunci Bahan Humik Asid Humik Penjerapan Sekam Padi Penjerap Poly
(Acrylamide) Carboxyl Modified Potassium Carbonate
Vlll
ABSTRACT
Nowadays consumers concern about the quality of water that being
supplied in order to ensure the water supplied is free from any harmful
substances like Humic Substances (HS) HS are divided into three main fractions
which are Humic Acid Fulvic Acid and Humin High concentration of Humic
Acid in drinking water can cause disease for human like stomach cancer Thus it
is important to develop a new technique to improve the quality of drinking water
Therefore adsorption method is the best way that can be used in order to remove
HS Moreover from the previous research activated carbon has been used to
remove HS but it is costly As an alternative way Rice husk has been used as an
adsorbent in the wastewater treatment compared to other agricultural waste due
to its structure and characteristics as adsorbent Heating and utilization of
chemical modifier like Poly (Acrylamide) Carboxyl Modified and Potassium
Carbonate can have a significant impact on adsorption of HS The result has
shown that rice husk which is treated with Poly (Acrylamide) Carboxyl Modified
occurs the highest rate of adsorption of HS because the Percentage of
Transmittance () of Carboxylic functional groups decreases as well as the
presence of Amine groups in the wastewater However for Aromatic groups
untreated rice husk become the best adsorbent for HS
Keyword Humic Substances Humic Acid Adsorption Rice Hush Adsorbent Poly
(Aery lam ide) Carboxyl Modified Potassium Carbonate
IX
iusat Khid a Mak1umat Akadtmil UNlVERSm MALAYSIA SARAWAJ(
TABLE OF CONTENTS
Pages
DECLARATION OF ORIGINAL WORK
APPROVAL SHEET III
ACKNOWLEDGEMENT Vll
ABSTRAK VllI
ABSTRACT LX
LIST OF TABLES XUI
NOMENCLATURE XVIll
APPROVAL CONFIDENTIAL LETTER IV
TITLE PAGE V
DEDICATION VI
TABLE OF CONTENTS x
LIST OF FIGURES XIV
ABBREVIATIONS XVI
CHAPTER 1 INTRODUCTION
11 General 1
111 Humic Substances 1
112 Main Component of Humic Substance 2
113 Effect on Humic Substances 3
114 Method of Filtrations of Humic Substance 3
115 Adsorption 4
116 Potential of Agricultural Waste in Malaysia 4
Type of Agricultural Waste 6
12 Problem Statements 8
13 Objectives 9
14 Methodology 10
15 Expected Outcome 12
X
shy---=-shy-
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
Pusat Khidmat Maklumat Akademh UNlVERSm MALAYSIA SARAWAJ(
STUDY ON THE POTENTIAL OF UTILIZING RICE HUSK AS
BIOSORBENT FOR HUMIC SUBSTANCE
SHARIFAH NURUL FAZILLA BINTI GHAZALI
Thesis is submitted to
Faculty of Engineering Universiti Malaysia Sarawak
In Partial Fulfilment of the Requirements
For the Degree of Bachelor of Engineering
Chemical Engineering (With Honours)
2013
v
I
I
Dedicated to my beloved dad and mom supervisor lecturers and friends
who always bestow me sustainable motivations inspirations and
encouragements
VI
ACKNOWLEDGEMENT
The author would like to express her sincerest appreciation to
supportive and helpful supervisor Mr Mohd Farid Atan for guidance
supports and valuables knowledge as well as for invaluable supervision
towards the completion of this research project The author also takes this
opportunity to express her gratitude to Co-Supervisor Mr Nazeri Abdul
Rahman and Dr Shanti Faridah Salleh for their willingness to give the
ideas and moral support along the implementation of the project Special
thanks are dedicated to authors family who always give her supports and
love Last but not least the authors would like to express her pleasure to
all of the staff from Department of Chemical Engineering amp Energy
Sustainability friends and all individuals that have contributed and
cooperated throughout in completing this project
Vll
ABSTRAK Pada masa kini pengguna mengambil berat tentang kualiti aIr yang
dibekalkan untuk memastikan ianya bebas daripada bahan berbahaya seperti
Bahan humik Bahan Humik mengandungi tiga (3) komponen utama iaitu Asid
Humik Asid Fulvik dan Humin Asid Humik berkepekatan tinggi di dalam air
minuman boleh menyebabkan penyakit kepada manusia seperti kanser perut
Justeru ia adalah penting untuk mengenalpasti satu kaedah baru untuk
meningkatkan kualiti air minuman Kaedah penjerapan adalah cara yang
terbaik yang dapat digunakan untuk memjerap Bahan Humik Berdasarkan
daripada hasil penyelidikan yang dijalankan sebelum ini Activated Carbon
digunakan untuk membuang Bahan Humik tetapi ianya menelan kos yang agak
tinggi Oleh itu sekam padi adalah penjerap terbaik di dalam merawat sisa
kumbahan berbanding dengan sisa pertanian yang lain Hal ini kerana struktur
dan sifat-sifat sekam padi sebagai penjerap Pemanasan dan pengubahsuaian
sekam padi dengan menggunakan Poly (Acrylamide) Carboxyl Modified dan
Potassium Carbonate mempunyai kesan signifikasi ke atas penjerapan Bahan
Humik Keputusan eksperimen menunjukkan kadar penjerapan yang tinggi
diperolehi dengan mencuci sekam padi dengan Poly (Acrylamide) Carboxyl
Modified kerana Peratusan Transmitansi () daripada kumpulan berfungsi
Karboksilik serta kumpulan Amine berkurangan Sebaliknya untuk kumpulan
Aromatik sekam padi yang tidak dirawat adalah penjerap cara terbaik untuk
penjerapan dalam Bahan Humik
Kata Kunci Bahan Humik Asid Humik Penjerapan Sekam Padi Penjerap Poly
(Acrylamide) Carboxyl Modified Potassium Carbonate
Vlll
ABSTRACT
Nowadays consumers concern about the quality of water that being
supplied in order to ensure the water supplied is free from any harmful
substances like Humic Substances (HS) HS are divided into three main fractions
which are Humic Acid Fulvic Acid and Humin High concentration of Humic
Acid in drinking water can cause disease for human like stomach cancer Thus it
is important to develop a new technique to improve the quality of drinking water
Therefore adsorption method is the best way that can be used in order to remove
HS Moreover from the previous research activated carbon has been used to
remove HS but it is costly As an alternative way Rice husk has been used as an
adsorbent in the wastewater treatment compared to other agricultural waste due
to its structure and characteristics as adsorbent Heating and utilization of
chemical modifier like Poly (Acrylamide) Carboxyl Modified and Potassium
Carbonate can have a significant impact on adsorption of HS The result has
shown that rice husk which is treated with Poly (Acrylamide) Carboxyl Modified
occurs the highest rate of adsorption of HS because the Percentage of
Transmittance () of Carboxylic functional groups decreases as well as the
presence of Amine groups in the wastewater However for Aromatic groups
untreated rice husk become the best adsorbent for HS
Keyword Humic Substances Humic Acid Adsorption Rice Hush Adsorbent Poly
(Aery lam ide) Carboxyl Modified Potassium Carbonate
IX
iusat Khid a Mak1umat Akadtmil UNlVERSm MALAYSIA SARAWAJ(
TABLE OF CONTENTS
Pages
DECLARATION OF ORIGINAL WORK
APPROVAL SHEET III
ACKNOWLEDGEMENT Vll
ABSTRAK VllI
ABSTRACT LX
LIST OF TABLES XUI
NOMENCLATURE XVIll
APPROVAL CONFIDENTIAL LETTER IV
TITLE PAGE V
DEDICATION VI
TABLE OF CONTENTS x
LIST OF FIGURES XIV
ABBREVIATIONS XVI
CHAPTER 1 INTRODUCTION
11 General 1
111 Humic Substances 1
112 Main Component of Humic Substance 2
113 Effect on Humic Substances 3
114 Method of Filtrations of Humic Substance 3
115 Adsorption 4
116 Potential of Agricultural Waste in Malaysia 4
Type of Agricultural Waste 6
12 Problem Statements 8
13 Objectives 9
14 Methodology 10
15 Expected Outcome 12
X
shy---=-shy-
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
I
I
Dedicated to my beloved dad and mom supervisor lecturers and friends
who always bestow me sustainable motivations inspirations and
encouragements
VI
ACKNOWLEDGEMENT
The author would like to express her sincerest appreciation to
supportive and helpful supervisor Mr Mohd Farid Atan for guidance
supports and valuables knowledge as well as for invaluable supervision
towards the completion of this research project The author also takes this
opportunity to express her gratitude to Co-Supervisor Mr Nazeri Abdul
Rahman and Dr Shanti Faridah Salleh for their willingness to give the
ideas and moral support along the implementation of the project Special
thanks are dedicated to authors family who always give her supports and
love Last but not least the authors would like to express her pleasure to
all of the staff from Department of Chemical Engineering amp Energy
Sustainability friends and all individuals that have contributed and
cooperated throughout in completing this project
Vll
ABSTRAK Pada masa kini pengguna mengambil berat tentang kualiti aIr yang
dibekalkan untuk memastikan ianya bebas daripada bahan berbahaya seperti
Bahan humik Bahan Humik mengandungi tiga (3) komponen utama iaitu Asid
Humik Asid Fulvik dan Humin Asid Humik berkepekatan tinggi di dalam air
minuman boleh menyebabkan penyakit kepada manusia seperti kanser perut
Justeru ia adalah penting untuk mengenalpasti satu kaedah baru untuk
meningkatkan kualiti air minuman Kaedah penjerapan adalah cara yang
terbaik yang dapat digunakan untuk memjerap Bahan Humik Berdasarkan
daripada hasil penyelidikan yang dijalankan sebelum ini Activated Carbon
digunakan untuk membuang Bahan Humik tetapi ianya menelan kos yang agak
tinggi Oleh itu sekam padi adalah penjerap terbaik di dalam merawat sisa
kumbahan berbanding dengan sisa pertanian yang lain Hal ini kerana struktur
dan sifat-sifat sekam padi sebagai penjerap Pemanasan dan pengubahsuaian
sekam padi dengan menggunakan Poly (Acrylamide) Carboxyl Modified dan
Potassium Carbonate mempunyai kesan signifikasi ke atas penjerapan Bahan
Humik Keputusan eksperimen menunjukkan kadar penjerapan yang tinggi
diperolehi dengan mencuci sekam padi dengan Poly (Acrylamide) Carboxyl
Modified kerana Peratusan Transmitansi () daripada kumpulan berfungsi
Karboksilik serta kumpulan Amine berkurangan Sebaliknya untuk kumpulan
Aromatik sekam padi yang tidak dirawat adalah penjerap cara terbaik untuk
penjerapan dalam Bahan Humik
Kata Kunci Bahan Humik Asid Humik Penjerapan Sekam Padi Penjerap Poly
(Acrylamide) Carboxyl Modified Potassium Carbonate
Vlll
ABSTRACT
Nowadays consumers concern about the quality of water that being
supplied in order to ensure the water supplied is free from any harmful
substances like Humic Substances (HS) HS are divided into three main fractions
which are Humic Acid Fulvic Acid and Humin High concentration of Humic
Acid in drinking water can cause disease for human like stomach cancer Thus it
is important to develop a new technique to improve the quality of drinking water
Therefore adsorption method is the best way that can be used in order to remove
HS Moreover from the previous research activated carbon has been used to
remove HS but it is costly As an alternative way Rice husk has been used as an
adsorbent in the wastewater treatment compared to other agricultural waste due
to its structure and characteristics as adsorbent Heating and utilization of
chemical modifier like Poly (Acrylamide) Carboxyl Modified and Potassium
Carbonate can have a significant impact on adsorption of HS The result has
shown that rice husk which is treated with Poly (Acrylamide) Carboxyl Modified
occurs the highest rate of adsorption of HS because the Percentage of
Transmittance () of Carboxylic functional groups decreases as well as the
presence of Amine groups in the wastewater However for Aromatic groups
untreated rice husk become the best adsorbent for HS
Keyword Humic Substances Humic Acid Adsorption Rice Hush Adsorbent Poly
(Aery lam ide) Carboxyl Modified Potassium Carbonate
IX
iusat Khid a Mak1umat Akadtmil UNlVERSm MALAYSIA SARAWAJ(
TABLE OF CONTENTS
Pages
DECLARATION OF ORIGINAL WORK
APPROVAL SHEET III
ACKNOWLEDGEMENT Vll
ABSTRAK VllI
ABSTRACT LX
LIST OF TABLES XUI
NOMENCLATURE XVIll
APPROVAL CONFIDENTIAL LETTER IV
TITLE PAGE V
DEDICATION VI
TABLE OF CONTENTS x
LIST OF FIGURES XIV
ABBREVIATIONS XVI
CHAPTER 1 INTRODUCTION
11 General 1
111 Humic Substances 1
112 Main Component of Humic Substance 2
113 Effect on Humic Substances 3
114 Method of Filtrations of Humic Substance 3
115 Adsorption 4
116 Potential of Agricultural Waste in Malaysia 4
Type of Agricultural Waste 6
12 Problem Statements 8
13 Objectives 9
14 Methodology 10
15 Expected Outcome 12
X
shy---=-shy-
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
ACKNOWLEDGEMENT
The author would like to express her sincerest appreciation to
supportive and helpful supervisor Mr Mohd Farid Atan for guidance
supports and valuables knowledge as well as for invaluable supervision
towards the completion of this research project The author also takes this
opportunity to express her gratitude to Co-Supervisor Mr Nazeri Abdul
Rahman and Dr Shanti Faridah Salleh for their willingness to give the
ideas and moral support along the implementation of the project Special
thanks are dedicated to authors family who always give her supports and
love Last but not least the authors would like to express her pleasure to
all of the staff from Department of Chemical Engineering amp Energy
Sustainability friends and all individuals that have contributed and
cooperated throughout in completing this project
Vll
ABSTRAK Pada masa kini pengguna mengambil berat tentang kualiti aIr yang
dibekalkan untuk memastikan ianya bebas daripada bahan berbahaya seperti
Bahan humik Bahan Humik mengandungi tiga (3) komponen utama iaitu Asid
Humik Asid Fulvik dan Humin Asid Humik berkepekatan tinggi di dalam air
minuman boleh menyebabkan penyakit kepada manusia seperti kanser perut
Justeru ia adalah penting untuk mengenalpasti satu kaedah baru untuk
meningkatkan kualiti air minuman Kaedah penjerapan adalah cara yang
terbaik yang dapat digunakan untuk memjerap Bahan Humik Berdasarkan
daripada hasil penyelidikan yang dijalankan sebelum ini Activated Carbon
digunakan untuk membuang Bahan Humik tetapi ianya menelan kos yang agak
tinggi Oleh itu sekam padi adalah penjerap terbaik di dalam merawat sisa
kumbahan berbanding dengan sisa pertanian yang lain Hal ini kerana struktur
dan sifat-sifat sekam padi sebagai penjerap Pemanasan dan pengubahsuaian
sekam padi dengan menggunakan Poly (Acrylamide) Carboxyl Modified dan
Potassium Carbonate mempunyai kesan signifikasi ke atas penjerapan Bahan
Humik Keputusan eksperimen menunjukkan kadar penjerapan yang tinggi
diperolehi dengan mencuci sekam padi dengan Poly (Acrylamide) Carboxyl
Modified kerana Peratusan Transmitansi () daripada kumpulan berfungsi
Karboksilik serta kumpulan Amine berkurangan Sebaliknya untuk kumpulan
Aromatik sekam padi yang tidak dirawat adalah penjerap cara terbaik untuk
penjerapan dalam Bahan Humik
Kata Kunci Bahan Humik Asid Humik Penjerapan Sekam Padi Penjerap Poly
(Acrylamide) Carboxyl Modified Potassium Carbonate
Vlll
ABSTRACT
Nowadays consumers concern about the quality of water that being
supplied in order to ensure the water supplied is free from any harmful
substances like Humic Substances (HS) HS are divided into three main fractions
which are Humic Acid Fulvic Acid and Humin High concentration of Humic
Acid in drinking water can cause disease for human like stomach cancer Thus it
is important to develop a new technique to improve the quality of drinking water
Therefore adsorption method is the best way that can be used in order to remove
HS Moreover from the previous research activated carbon has been used to
remove HS but it is costly As an alternative way Rice husk has been used as an
adsorbent in the wastewater treatment compared to other agricultural waste due
to its structure and characteristics as adsorbent Heating and utilization of
chemical modifier like Poly (Acrylamide) Carboxyl Modified and Potassium
Carbonate can have a significant impact on adsorption of HS The result has
shown that rice husk which is treated with Poly (Acrylamide) Carboxyl Modified
occurs the highest rate of adsorption of HS because the Percentage of
Transmittance () of Carboxylic functional groups decreases as well as the
presence of Amine groups in the wastewater However for Aromatic groups
untreated rice husk become the best adsorbent for HS
Keyword Humic Substances Humic Acid Adsorption Rice Hush Adsorbent Poly
(Aery lam ide) Carboxyl Modified Potassium Carbonate
IX
iusat Khid a Mak1umat Akadtmil UNlVERSm MALAYSIA SARAWAJ(
TABLE OF CONTENTS
Pages
DECLARATION OF ORIGINAL WORK
APPROVAL SHEET III
ACKNOWLEDGEMENT Vll
ABSTRAK VllI
ABSTRACT LX
LIST OF TABLES XUI
NOMENCLATURE XVIll
APPROVAL CONFIDENTIAL LETTER IV
TITLE PAGE V
DEDICATION VI
TABLE OF CONTENTS x
LIST OF FIGURES XIV
ABBREVIATIONS XVI
CHAPTER 1 INTRODUCTION
11 General 1
111 Humic Substances 1
112 Main Component of Humic Substance 2
113 Effect on Humic Substances 3
114 Method of Filtrations of Humic Substance 3
115 Adsorption 4
116 Potential of Agricultural Waste in Malaysia 4
Type of Agricultural Waste 6
12 Problem Statements 8
13 Objectives 9
14 Methodology 10
15 Expected Outcome 12
X
shy---=-shy-
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
ABSTRAK Pada masa kini pengguna mengambil berat tentang kualiti aIr yang
dibekalkan untuk memastikan ianya bebas daripada bahan berbahaya seperti
Bahan humik Bahan Humik mengandungi tiga (3) komponen utama iaitu Asid
Humik Asid Fulvik dan Humin Asid Humik berkepekatan tinggi di dalam air
minuman boleh menyebabkan penyakit kepada manusia seperti kanser perut
Justeru ia adalah penting untuk mengenalpasti satu kaedah baru untuk
meningkatkan kualiti air minuman Kaedah penjerapan adalah cara yang
terbaik yang dapat digunakan untuk memjerap Bahan Humik Berdasarkan
daripada hasil penyelidikan yang dijalankan sebelum ini Activated Carbon
digunakan untuk membuang Bahan Humik tetapi ianya menelan kos yang agak
tinggi Oleh itu sekam padi adalah penjerap terbaik di dalam merawat sisa
kumbahan berbanding dengan sisa pertanian yang lain Hal ini kerana struktur
dan sifat-sifat sekam padi sebagai penjerap Pemanasan dan pengubahsuaian
sekam padi dengan menggunakan Poly (Acrylamide) Carboxyl Modified dan
Potassium Carbonate mempunyai kesan signifikasi ke atas penjerapan Bahan
Humik Keputusan eksperimen menunjukkan kadar penjerapan yang tinggi
diperolehi dengan mencuci sekam padi dengan Poly (Acrylamide) Carboxyl
Modified kerana Peratusan Transmitansi () daripada kumpulan berfungsi
Karboksilik serta kumpulan Amine berkurangan Sebaliknya untuk kumpulan
Aromatik sekam padi yang tidak dirawat adalah penjerap cara terbaik untuk
penjerapan dalam Bahan Humik
Kata Kunci Bahan Humik Asid Humik Penjerapan Sekam Padi Penjerap Poly
(Acrylamide) Carboxyl Modified Potassium Carbonate
Vlll
ABSTRACT
Nowadays consumers concern about the quality of water that being
supplied in order to ensure the water supplied is free from any harmful
substances like Humic Substances (HS) HS are divided into three main fractions
which are Humic Acid Fulvic Acid and Humin High concentration of Humic
Acid in drinking water can cause disease for human like stomach cancer Thus it
is important to develop a new technique to improve the quality of drinking water
Therefore adsorption method is the best way that can be used in order to remove
HS Moreover from the previous research activated carbon has been used to
remove HS but it is costly As an alternative way Rice husk has been used as an
adsorbent in the wastewater treatment compared to other agricultural waste due
to its structure and characteristics as adsorbent Heating and utilization of
chemical modifier like Poly (Acrylamide) Carboxyl Modified and Potassium
Carbonate can have a significant impact on adsorption of HS The result has
shown that rice husk which is treated with Poly (Acrylamide) Carboxyl Modified
occurs the highest rate of adsorption of HS because the Percentage of
Transmittance () of Carboxylic functional groups decreases as well as the
presence of Amine groups in the wastewater However for Aromatic groups
untreated rice husk become the best adsorbent for HS
Keyword Humic Substances Humic Acid Adsorption Rice Hush Adsorbent Poly
(Aery lam ide) Carboxyl Modified Potassium Carbonate
IX
iusat Khid a Mak1umat Akadtmil UNlVERSm MALAYSIA SARAWAJ(
TABLE OF CONTENTS
Pages
DECLARATION OF ORIGINAL WORK
APPROVAL SHEET III
ACKNOWLEDGEMENT Vll
ABSTRAK VllI
ABSTRACT LX
LIST OF TABLES XUI
NOMENCLATURE XVIll
APPROVAL CONFIDENTIAL LETTER IV
TITLE PAGE V
DEDICATION VI
TABLE OF CONTENTS x
LIST OF FIGURES XIV
ABBREVIATIONS XVI
CHAPTER 1 INTRODUCTION
11 General 1
111 Humic Substances 1
112 Main Component of Humic Substance 2
113 Effect on Humic Substances 3
114 Method of Filtrations of Humic Substance 3
115 Adsorption 4
116 Potential of Agricultural Waste in Malaysia 4
Type of Agricultural Waste 6
12 Problem Statements 8
13 Objectives 9
14 Methodology 10
15 Expected Outcome 12
X
shy---=-shy-
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
ABSTRACT
Nowadays consumers concern about the quality of water that being
supplied in order to ensure the water supplied is free from any harmful
substances like Humic Substances (HS) HS are divided into three main fractions
which are Humic Acid Fulvic Acid and Humin High concentration of Humic
Acid in drinking water can cause disease for human like stomach cancer Thus it
is important to develop a new technique to improve the quality of drinking water
Therefore adsorption method is the best way that can be used in order to remove
HS Moreover from the previous research activated carbon has been used to
remove HS but it is costly As an alternative way Rice husk has been used as an
adsorbent in the wastewater treatment compared to other agricultural waste due
to its structure and characteristics as adsorbent Heating and utilization of
chemical modifier like Poly (Acrylamide) Carboxyl Modified and Potassium
Carbonate can have a significant impact on adsorption of HS The result has
shown that rice husk which is treated with Poly (Acrylamide) Carboxyl Modified
occurs the highest rate of adsorption of HS because the Percentage of
Transmittance () of Carboxylic functional groups decreases as well as the
presence of Amine groups in the wastewater However for Aromatic groups
untreated rice husk become the best adsorbent for HS
Keyword Humic Substances Humic Acid Adsorption Rice Hush Adsorbent Poly
(Aery lam ide) Carboxyl Modified Potassium Carbonate
IX
iusat Khid a Mak1umat Akadtmil UNlVERSm MALAYSIA SARAWAJ(
TABLE OF CONTENTS
Pages
DECLARATION OF ORIGINAL WORK
APPROVAL SHEET III
ACKNOWLEDGEMENT Vll
ABSTRAK VllI
ABSTRACT LX
LIST OF TABLES XUI
NOMENCLATURE XVIll
APPROVAL CONFIDENTIAL LETTER IV
TITLE PAGE V
DEDICATION VI
TABLE OF CONTENTS x
LIST OF FIGURES XIV
ABBREVIATIONS XVI
CHAPTER 1 INTRODUCTION
11 General 1
111 Humic Substances 1
112 Main Component of Humic Substance 2
113 Effect on Humic Substances 3
114 Method of Filtrations of Humic Substance 3
115 Adsorption 4
116 Potential of Agricultural Waste in Malaysia 4
Type of Agricultural Waste 6
12 Problem Statements 8
13 Objectives 9
14 Methodology 10
15 Expected Outcome 12
X
shy---=-shy-
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
iusat Khid a Mak1umat Akadtmil UNlVERSm MALAYSIA SARAWAJ(
TABLE OF CONTENTS
Pages
DECLARATION OF ORIGINAL WORK
APPROVAL SHEET III
ACKNOWLEDGEMENT Vll
ABSTRAK VllI
ABSTRACT LX
LIST OF TABLES XUI
NOMENCLATURE XVIll
APPROVAL CONFIDENTIAL LETTER IV
TITLE PAGE V
DEDICATION VI
TABLE OF CONTENTS x
LIST OF FIGURES XIV
ABBREVIATIONS XVI
CHAPTER 1 INTRODUCTION
11 General 1
111 Humic Substances 1
112 Main Component of Humic Substance 2
113 Effect on Humic Substances 3
114 Method of Filtrations of Humic Substance 3
115 Adsorption 4
116 Potential of Agricultural Waste in Malaysia 4
Type of Agricultural Waste 6
12 Problem Statements 8
13 Objectives 9
14 Methodology 10
15 Expected Outcome 12
X
shy---=-shy-
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
CHAPTER 2 LITERATURE REVIEW
21 Rice Husk as Adsorbent 13
22 Humic Substances 15
221 Humic Acid 16
222 Fulvic Acid 17
223 Humin 18
23 Adsorption 19
231 Theory 19
232 Mathematical Modelling 20
233 Adsorption of Humic Substance 23
24 Chemical Modification Techniques of Rice Husk 24
241 Poly (Acrylamide) Carboxyl Modified 24
242 Potassium Carbonate 25
25 Impact on Related Parameter 25
251 Impact of Contact Time 25
252 Impact on pH 26
253 Effect of Initial Concentration 26
26 Analytical Instrument 27
261 Fourier Transform Infrared Spectrometry 27
(FT-IR)
262 Moisture Balance 30
CHAPTER 3 METHODOLOGY
31 Literature Review 32
32 Collect and Process Agriculture Waste 32
33 Propose Process Agriculture Wastes 33
34 Collect Wastewater Sample 34
35 Analysis Sample 34
36 Adsorption Process 35
37 Analysis Treated Sample 35
38 Results 36
Xl
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
CHAPTER 4 EXPERIMENTAL DESIGN
41 Preparation of the Fibre 37
42 Cleaning with Chemical Modifier 39
43 Preparation of the Wastewater 40
44 Mixed Fibre and Wastewater 41
45 Continuous Stirrer Tank Reactor (CSTR) 41
46 Collection of the sample 43
47 Analysis the samples 44
CHAPTER 5 RESULTS amp DISCUSSION
51 Sample of the Fibre and Wastewater 45
52 Adsorption of Humic Substance in Fibre 47
53 Impact of Temperature 49
54 Impact on Chemical Modifier 51
55 Structure of the Rice Husk 54
CHAPTER 6 CONCLUSION amp RECOMMENDATION
61 Conclusion 56
62 Recommendation 57
REFERENCES 58
APPENDIX GANTT CHART 68
xu
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
I
LIST OF TABLES
PageTable
Approximate Estimate of Annual Production of Agricultural 511
Waste and Residues in Selected Countries in the Region
12 Total Biomass Waste Available For Power Generation (ktonne) 6
21 Chemical Properties of Rice Husk 14
22 Characteristic of IR Absorption 29
Xlli
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
LIST OF FIGURES
Figure Page
11 Intensity colours of Humic Substance 2
Proportionate Annual Productions of Agricultural Wastes in 12 7
Malaysia
13 Methodology 10
21 Example of the Rice Husk 13
22 Model Structure of Humic Acid 17
23 Model Structure of Fulvic Acid 18
24 Moisture Balance 31
31 Flow Chart of Methodology 33
41 Flow of the Experiment has been Conducted 38
42 Potassium Carbonate diluted with Distilled Water 40
43 PID Controller Page at CSTR 42
44 Overview Page of CSTR 43
45 Example of the Sample Placed inside Petri Dish 44
51 Conditions of The Experiments 45
52 Functional Group Content inside Fibre of the Rice Husk 46
53 Functional Group of the Sample of Wastewater 46
Adsorption of Aromatic Groups Without Chemical and at Room 54 47
Condition
Adsorption of Carboxylic Groups Without Chemical and at Room 55 48
Condition
56 Impacts on Temperature of Without Chemical for Carboxylic Acid 49
xiv
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
I
I
I
Impacts on Temperature of Poly (Acrylamide) Carboxyl Modified
57 for 51
Amine
Impact on Chemical Modifier at Condition 60 oC for Amine 58 52
Group
Impact on Chemical Modifier at Condition 60 oC for Carboxylic 59 53
Group
510 Structure of the Rice Husk 56
xv
I
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
I
aF
aL
KL
q
aR
KR
bR
q
C
degC
COOH
CSTR
FT-IR
GAC
HS
IR
OH
OPEFB
PAC
PID
POME
I
ABBREVIATIONS
Freundlich Isotherm Constant
Langmuir Isotherm Constant
Langmuir Isotherm Constant
Langmuir Monolayer Saturation Capacity
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Constant
Redlich-Peterson Isotherm Exponent
Solid Phase Metal Ion Concentration At Equilibrium
Solution Phase Metal Ion Concentration At Equilibrium
Celcius
Carboxylic Group
Continuous Stirrer Tank Reactor
Fourier Transform Infrared Spectrometry
Granular Activated Carbon
Humic Substances
Infrared
Alcohol Group
Oil Palm Empty Fruit Bunch
Powdered Activated Carbon
Proportional Derivative and Integral
Palm Oil Mill Effluent
XVI
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
RHA Rice Husk Ash
SCORE Sarawak Corridor of Renewable Energy
XVll
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
NOMENCLATURE
cm Centimetre
Igm-3 Microgram per meter cubic
dm3g-1 Decimetre cubic per gram
dm3mmol-l Decimetre cubic per milimol
g Gram
ktonne kilotonne
mglL Mailgram per liter
mIn Minute
mL Mililitre
mmoldm-3 Milimol per decimetre cubic
Mmolg- Milimol per gram
Nm-2 Newton per meter square
ppb Part per billion
V Volt
XVllI
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
CHAPTER 1
INTRODUCTION
11 General
This chapter generally discuss about the overview of the research study
including introduction to Humic Substance Agricultural Waste and slightly on
adsorption process Problem Statement Objective Methodology and Expected
Outcome also been discussed in this Chapter in order to give some ideas on the
research study
111 Humic Substances
Environmental pollution has extremely increased in Malaysia especially
in water pollution Water is one of the important needs of human on this earth
Nowadays consumer are stressing on the quality of water which is supplied to
them in order to ensure that the water supplied is free from any harmful
substances like Humic Substances (HS) HS are the most widely distributed
products from biosynthesis contained in soil Apart from soil it also can be found
at different level of concentrations in different sources like rivers lakes oceans
compost sediments peat bogs and soft coal HS are formed by a process called
H umicification [1]
1
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
112 Main Component of Humic Substance
Humic substances (HS) consists of three (3) mam fractions which are
Humic Acid Fulvic Acid and Humin It can be classified based on it solubility in
acids and alkaline [2] Humic Acid is the first fraction of HS which is insoluble
in water under acidic conditions where pH is less than two (2) However it is
soluble at high value of pH where the value is more than ten (10) [2] Moreover
it consists of complex aromatic macromolecules and classified as the most
dominant group in HS Contrary Fulvic Acid which is the second fraction of HS
possesses different properties compared to Humic Acid It is soluble in water
under acidic and alkaline conditions Lastly Humin which is the third fraction
of HS is insoluble in water at any pH value Different components of HS are
identified by different intensity of colours as shown in Figure ll
Humic substances (pigmented polymers)
j FuMc acid
Lt-rl I 13riV
tit I black I
Light
yellow
----- increase in intensity of colour ) increase in degree of polymerization --~)
2 000----- increase in molecular weight ) 300000 45 increase in carbon content ) 62 48 decrease in oxygen content ) 30
1 400 decrease in exchange acidity ) 500 ----- decrease in degree of solubility ------lraquo
Figure l1 Intensity colours of Humic Substance [3]
2
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
113 Effect on Humic Substances
High concentration of Humic Acid in drinking water can cause some
serious diseases on human health like stomach cancer This is because it can
produce disinfection caused by by-products like trihalomethanes [4 5 6] Humic
Acid contains relatively high amount of basic Amino combination of functional
groups of Amine and Carboxylic Acid can be poisonous if the molecular weight of
Amines is relatively low [7 8] On the other hand Amines are not totally
harmful but when it reacts with other compounds it will form nitrosamines and
nitramines which have an irreversible effect on environment human and
animals Some of the amino compounds have also been known or suspected
carcinogens due to the aromatic amine which can cause disease like bladder
infection [9] Therefore it is important to remove HS especially Humic Acid from
drinking water As mentioned by Hatam et aI high amount of Humic Acid can
become one of the etiological factors for Blackfoot disease [10] For that reason
mineralization of the drinking water and other relevant process water in
treating Humic Acids are very essential
114 Method of Filtrations of Humic Substance
The conventional drinking water treatment processes like coagulation
settling and sand filtration can remove between 20 to 50 dissolved HS [11]
There are some various treatment techniques that are available for organic
compounds like reduction ion exchange evaporation reverse osmosis and
cbemical precipitation Most of these methods are highly expensive in term of
operating cost Moreover traditional drinking water treatment processes might
3
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
not be able to totally remove the organic compound Thus previous researcher
recommend that activated carbon can be used in order to remove the organic
compound like Humic Acid from water In Malaysia activated carbon is
produced from various materials like rubber wood sawdust and palm oil coconut
shell [12] Activated carbon is used primarily as an adsorbent with the aim of
removing organic compounds and pollutant from liquid and gas streams As an
alternative method agriculture waste is used as an adsorbent for the adsorption
of Humic Acid from drinking water
115 Adsorption
Adsorption is a physical process where gas or liquid solute accumulates
on the surface of a solid or a liquid which is known as adsorbent and forming a
molecular or atomic films which are known as adsorbate Adsorption is operative
in most natural physical biological and chemical systems It is also widely used
in industrial applications especially in water purification Adsorption is a
consequence of surface energy Adsorption is one the effective method that has
been used with the aim ofremoving Humic Acid from drin_king water [13]
116 Potential of Agricultural Waste in Malaysia
Improper disposal methods of agricultural wastes can cause serIOUS
environmental pollution [14] Instead of using Activated Carbon as an adsorbent
which is relatively expensive agricultural waste can be used as an alternative
adsorbent in order to remove Humic Acids from wastewater Recently the
4
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5
rusat Khitimat N aidumat Akademi UNlVERSm MALAyenSIA SARAWAK
interest in using low cost adsorbent for adsorption is largely augmented
According to Sadon et aI compared to conventional adsorbent this type of
natural adsorbents possesses a lot of advantages such as inexpensive effective
readily and local available technical feasibility as well as engineering
applicability [15] Expanding the agricultural production resulted in increased
quantities of livestock waste as shown in Table 11 provides an estimate of
annual production of agricultural waste and residues in some selected countries
in the region Based on the data Malaysia produced about 12 million tonnes
agricultural waste per annum and it considered as moderate compared to other
countries [16]
Table 11 Approximate Estimate of Annual Production of Agricultural Waste
and Residues in Selected Countries in the Region [16]
Country
Annual Production (million tonnes)
Agricultural Waste (Manure Animal Dung)
Crop Residues
Total
Bangladesh 15 30 45 Republic of China 255 587 842
India 240 320 560 Indonesia 32 90 122 Malaysia 12 30 42 Myanmar 28 4 32
Nepal 4 12 16 Pakistan 16 68 84
Philippines 2 12 32 Republic of Korea 15 10 25
Sri Lanka 6 3 9 Thailand 25 47 72
Waste is an unavoidable by-product generated from the majority of
human activity Generally the developed countries generate much more
quantities of waste per capita than developing countries like Malaysia [16]
However in certain conditions the management of small quantities of waste is
5