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UNIVERSITI PUTRA MALAYSIA
EVALUATING THE POTENTIAL OF BANK INFILTRATION AS A SOURCE OF WATER SUPPLY IN JENDERAM HILIR, SELANGOR, MALAYSIA
MOHD KHAIRUL NIZAR BIN SHAMSUDDIN
FPAS 2014 3
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EVALUATING THE POTENTIAL OF BANK INFILTRATION AS A
SOURCE OF WATER SUPPLY IN JENDERAM HILIR, SELANGOR,
MALAYSIA
By
MOHD KHAIRUL NIZAR BIN SHAMSUDDIN
Thesis Submitted to the School of Graduate Studies, Universiti Putra Malaysia,
in Fulfillment of the Requirements for the Master of Science
July 2014
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All material contained within the thesis, including without limitation text, logos,
icons, photographs and all other artwork, is copyright material of Universiti Putra
Malaysia unless otherwise stated. Use may be made of any material contained within
the thesis for non-commercial purposes from the copyright holder. Commercial use
of material may only be made with the express, prior, written permission of
Universiti Putra Malaysia.
Copyright © Universiti Putra Malaysia
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Abstract of thesis presented to the Senate of Universiti Putra Malaysia in fulfillment of the
requirement for the degree of Master of Science
EVALUATING THE POTENTIAL OF BANK INFILTRATION AS A SOURCE OF
WATER SUPPLY IN JENDERAM HILIR, SELANGOR, MALAYSIA
By
MOHD KHAIRUL NIZAR BIN SHAMSUDDIN
July 2014
Chairman : Wan Nor Azmin Sulaiman, PhD
Faculty : Environmental Studies
ABSTRACT
This study was inspired by the Klang Valley water crisis, for which Bank Infiltration (BI)
was considered as a potential solution. Higher incidences of pollution to the rivers in
Malaysia has lead to the decrease in resources for drinking water. Many developing countries
like Malaysia, are faced with a big challenge to provide safe drinking water to the ever-
increasing population. Currently, the treatment of river water uses chemicals to reduce
several contaminants due to pollution. The chemical contents could give long term effects to
the health of the consumers. However, there is hope in a more effective, but low-cost
technology, known as Bank Infiltration (BI) or Riverbank Filtration (RBF). BI is a natural
process using natural soil (aquifer) to treat river water and at the same time utilizes
groundwater. Moreover, due to its ability to remove even the most persistent contaminants
and microbes, BI can enhance treatment steps in a water treatment facilities, especially in a
conventional water treatment. BI is a method that has long been known but it is still new and
has not been practiced in Malaysia. Nevertheless, BI is site specific and requires thorough site
investigations to assess its feasibility based on the local site characteristics. The study area
was located in the southwest state of Selangor within the Langat Basin which covered an area
of 10 km2.
Besides, this study was specifically conducted to explore the possibility of using the BI
systems to source the polluted surface water with groundwater. Three major factors were
considered for evaluation: (i) an investigation on the contribution of surface water through
BI, (ii) the input of local groundwater, and (iii) the water quality characteristics of water
supply. In the earlier part of the investigations, the geophysical method was employed to
define the subsurface geology and hydrogeology of the area. Isotope techniques were
performed to identify the source of groundwater recharge and interaction between the surface
water and the groundwater. A total of 25 monitoring wells and 2 test wells (DW1 and DW2)
were constructed to circumscribe the BI system. The physicochemical and microbiological
parameters of the local surface water bodies and groundwater were analysed before and
during the water abstraction. The abstraction of water revealed a 5–98% decrease in turbidity,
as well as HCO3-, SO4
-, NO3-, Al, As and Ca concentrations reduction compared to the
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Langat River water. However, the water samples from test wells during pumping showed
high concentrations of Fe2+ and Mn2+. In addition, the amounts of E. coli, total coliform, and
Giardia were significantly reduced (99.9%).The pumping test results indicated that the two
test wells (DW1 and DW2) were able to sustain yields of 15.9 and 128 m3/hr, respectively.
The BI method looks closely at surface water and groundwater interaction. The water quality
interaction was assessed through multivariate statistical analyses based on analytical
quantitative data. Multivariate statistical analyses were used, including discriminant analysis
(DA) and principal component analysis (PCA), based on 36 water quality parameters from
the rivers, lakes, and groundwater sites at Jenderam Hilir, which were collected from 2009 to
2011 (56 observations). The DA identified six significant parameters (pH, NO2, NO3, F, Fe,
and Mn) from 36 variables to distinguish between the river, lake, and groundwater groups
(classification accuracy = 98%). The PCA confirmed and identified 10 possible causes of
variation in the groundwater quality with an eigenvalue greater than 1, which explained
82.931% of the total variance in the water quality data set: hydrochemistry; redox conditions;
groundwater flow; surface runoff; groundwater contact with rock or weathered rock (Kenny
Hills Formation); river water and groundwater interaction, discharge of untreated sewage and
industrial wastes into the river; interaction between the river, lake, and groundwater; heavy
metal pollution from past mining activities; and industrial pollution, such as dye or paint
operations. Hence, in order to evaluate the effects of groundwater pumping and BI operation
on the operations of wells, as well as to determine the effects of pumping rate on flow paths,
travel time, size of pumping, and to capture zone delineation and groundwater mixing in a
pumping well, numerical modelling simulation using MODFLOW and MODPATH were
used. The simulation involved trying different scenarios by changing the variables to perform
infiltration safely and to achieve the ideal pumping rate. The results indicated that the
migration of river water into the aquifer has been generally slow and depended on the
pumping rate and the distance from the pumping well to the river. Most water arrived at the
well by the end of the pumping period of 1 to 5 days at 3072 m3/day for test wells of DW1
and DW2, and during the simultaneous pumping for DW2 and PW1 for a well located 40 m
and 20 m, respectively, from the river. During the 9.7-day pumping period, 33% of the water
pumped from the DW1 well was river water, and 38% percent of the water pumped from
DW2 throughout 4.6 days was river water. The models provided necessary information to
water operators in the design, and the construction of pumping and sampling schedules of the
BI practices. The detailed field investigation programmes obtained from this study can be
used for preliminary BI system design and pilot construction by stakeholders, water operator
or related agencies in Malaysia, as the study provided good methods and investigation
(geophysical, isotope, grain size analysis, colloidal borescope systems and water quality
analysis). The statistical and numerical methods to study the BI may also be used in other
areas of similar hydrological characteristics and climate conditions.
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Abstrak tesis yang dikemukakan kepada Senat Universiti Putra Malaysia sebagai memenuhi
keperluan untuk ijazah Master Sains
MENILAI POTENSI SUSUPAN TEBING SEBAGAI SUMBER BEKALAN AIR DI
JENDERAM HILIR, SELANGOR, MALAYSIA
Oleh
MOHD KHAIRUL NIZAR BIN SHAMSUDDIN
Julai 2014
Pengerusi : Wan Nor Azmin Sulaiman , PhD
Fakulti : Pengajian Alam Sekitar
ABSTRAK
Kajian ini diilhamkan oleh krisis air Lembah Klang, yang mana Susupan Tebing (BI) adalah
dianggap sebagai penyelesaian yang berpotensi. Insiden yang lebih tinggi daripada
pencemaran sungai di Malaysia boleh membawa kepada pengurangan dalam sumber untuk
air minuman. Banyak negara-negara membangun, seperti Malaysia, berhadapan dengan
cabaran yang besar untuk menyediakan air minuman yang selamat kepada penduduk yang
semakin meningkat. Pada masa ini, rawatan air sungai menggunakan bahan kimia untuk
mengurangkan beberapa bahan cemar akibat pencemaran. Kandungan kimia boleh memberi
kesan jangka panjang kepada kesihatan pengguna. Bagaimanapun, teknologi terkini yang
lebih berkesan yang menggunakan kos yang lebih rendah dikenali sebagai Susupan Tebing
(BI) atau Sistem Penapisan Tebingan Sungai (RBF). BI adalah proses semulajadi
menggunakan tanah (akuifer) untuk merawat air sungai dan pada masa yang sama
menggunakan air tanah. Oleh kerana keupayaan untuk menyingkirkan bahan-bahan pencemar
dan mikrob, BI sebagai sokongan kepada sebahagian skim rawatan air terutamanya dalam
rawatan air secara konvensional. BI adalah kaedah yang telah lama diketahui tetapi masih
baru dan tidak diamalkan di Malaysia. Walau bagaimanapun, BI adalah bergantung kepada
kawasan yang spesifik dan memerlukan penyiasatan tapak secara terperinci bagi menilai
kebolehkesanan ciri-ciri setempat. Kawasan kajian ini terlatak di baratdaya Negeri Selangor
di dalam lembangan Sungai Langat yang meliputi kawasan seluas 10 km2.
Di samping itu, kajian ini dijalankan khusus untuk mengkaji keupayaan penggunaan sistem
BI sebagai penapis sumber air permukaan yang tercemar bersama-sama dengan air tanah.
Tiga faktor utama yang telah dipertimbangkan untuk penilaian: (i) Kajian mengenai kaitan air
permukaan melalui BI (ii) input air tanah tempatan, dan (iii) ciri-ciri kualiti air sebagai
bekalan air. Sebagai permulaan kaijan, kaedah geofizik telah digunakan untuk menentukan
geologi subpermukaan dan hidrogeologi di kawasan kajian. Teknik isotop telah dijalankan
untuk mengenal pasti punca imbuhan air tanah dan interaksi di antara air permukaan dan air
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tanah. Sejumlah 25 telaga pemantauan dan 2 telaga ujian telah dibina dalam menentukan
sistem BI. Parameter fizikokimia dan mikrobiologi air permukaan dan air tanah setempat
telah dianalisis sebelum dan semasa abstraksi air. Abstraksi air menunjukkan penurunan
kekeruhan sebanyak 5%-98%, serta pengurangan kepekatan HCO3-, SO4
-, NO3-, Al, As, dan
Ca berbanding dengan air Sungai Langat. Walau bagaimanapun, sampel air dari telaga ujian
semasa ujian pengepaman dilakukan, menunjukkan kepekatan Fe2+ dan Mn2+ yang tinggi. Di
samping itu, jumlah E. coli, koliform dan Giardia telah berkurangan dengan ketara (99.9 %).
Keputusan ujian pengepaman menunjukkan bahawa kedua-dua telaga (DW1 dan DW2)
mampu mencapai kadar mampan abstraksi air sebanyak 15.9 dan 128 m3/jam.
Kaedah BI adalah interaksi yang begitu rapat antara air permukaan dan interaksi air tanah.
Interaksi kualiti air telah dinilai melalui analisis statistik multivariat berdasarkan data
kuantitatif analisis. Analisis statistik multivariat telah digunakan, termasuk analisis
diskriminan (DA) dan analisis komponen utama (PCA), berdasarkan 36 parameter kualiti air
dari sungai, tasik, dan air tanah di Jenderam Hilir yang dilakukan dari tahun 2009-2011 (56
cerapan). DA telah mengenal pasti enam parameter penting (pH, NO2, NO3, F, Fe dan Mn)
daripada 36 pembolehubah untuk membezakan di antara sungai, tasik, dan air tanah
(ketepatan pengelasan = 98%). PCA mengesahkan dan mengenal pasti sepuluh kemungkinan
punca perubahan dalam kualiti air tanah dengan nilai eigen yang lebih besar daripada 1 yang
menjelaskan 82.931 % daripada jumlah perbezaan dalam set data kualiti air: hidrokimia;
keadaan redoks; aliran air tanah; air larian permukaan, sentuhan air tanah dengan batuan atau
batuan terluluhawa (Formasi Kenny Hills); interaksi air sungai dan air tanah, serta pelepasan
air kumbahan yang tidak dirawat dan sisa industri ke dalam sungai; interaksi antara sungai,
tasik dan air tanah, pencemaran logam berat daripada aktiviti perlombongan; dan pencemaran
industri seperti daripada aktiviti pembuatan cat atau pewarna. Dalam usaha untuk menilai
kesan pengepaman air tanah dan operasi BI terhadap keupayaan telaga dan juga untuk
menentukan kesan kadar pengepaman keatas arah aliran, masa pergerakan aliran air, kesan
pengepaman didalam zon sempadan pemerangkapan dan zon campuran air tanah, simulasi
numerikal menggunakan MODFLOW dan MODPATH digunakan. Simulasi ini terdiri
daripada pelbagai senario yang berbeza dengan mengubah pembolehubah untuk menentukan
nilai penyusupan yang selamat dan mencapai kadar pengepaman yang sesuai. Keputusan
menunjukkan bahawa migrasi air sungai ke dalam akuifer umumnya perlahan dan bergantung
kepada kadar pengepaman dan jarak dari telaga pengepaman ke sungai. Kebanyakan air
sampai di telaga pada akhir tempoh pengepaman 1 hingga 5 hari pada kadar 3072 m3/hari
bagi telaga ujian DW1 dan DW2, dan semasa pengepaman serentak bagi DW2 dan PW1
yang terletak kira-kira 40m dan 20m dari sungai. Semasa tempoh pengepaman selama 9.7
hari, 33% daripada air yang dipam dari DW1 adalah air sungai, dan 38% peratus air yang
dipam selama 4.6 hari bagi DW2, adalah air sungai. Pemodelan ini menyediakan maklumat
yang diperlukan untuk operator air dalam mereka bentuk dan merancang jadual pengepaman
dan persampelan ke atas sistem BI. Siasatan terperinci hasil yang diperolehi dari kajian ini boleh
digunapakai untuk merekabentuk sistem BI dan pembinaan perintis ini oleh pihak
berkepentingan seperti operator air atau agensi-agensi yang berkaitan di Malaysia, seperti
kaedah kajian yang dilakukan ini amat sesuai digunakan dalam penyelidikan (geofizik,
isotop, analisis saiz butiran, boroskopi koloid sistem dan analisis kualiti air). Kaedah statistik
dan berangka untuk mengkaji BI boleh juga digunakan di kawasan-kawasan lain yang
mempunyai ciri-ciri hidrologi dan keadaan iklim yang sama.
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ACKNOWLEDGEMENTS
I would to take this opportunity to thank Prof Dr Wan Azmin Sulaiman, Prof Dr Mohammad
Pauzi, Dr Saim Suratman and Dr. Kamarudin Samuding for giving me valuable suggestions
and continuous encouragement during the preparation of this thesis. I wish to thank all other
staff of the Faculty of Environment, University of Putra Malaysia who has helped me during
the years of the study here.
I would like to thank a number of research officer at the National Hydraulic Research
Institute of Malaysia (NAHRIM) especially Mr. Azrul Normi, Mr. Anuar Sefie, Mr. Huzaifah
Wahab, Mr. Ali Sarudin and Mr. Syaiful Bahren Saadudin who has helped me in getting all
the related data on Bank Infiltration study and who has helped and accompanying me in the
field works.
Thanks also to the staff of the Minerals and Geoscience Malaysia (JMG), Selangor who have
directly or indirectly helped me during data collection.
I would also like to thank the Malaysian Meteorological Department (JMM), Drainage and
Irrigation Department (DID) and Department of Environment (DOE) for allowing me access
to essential hydrological and environmental data which they hold.
Lastly, the warmest thank to my dearest wife, Mrs Zurina Salleh and my lovely daughters Ms
Nur Damia Husna who have been very supportive during the preparation of this thesis.
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APPROVAL
I certify that a Thesis Examination Committee has met on (17 July 2014) to conduct the final
examination of Mohd Khairul Nizar Bin Shamsuddin on his thesis entitled "Evaluating the
Potential of Bank Infiltration as A Source Of Water Supply In Jenderam Hilir, Selangor,
Malaysia" in accordance with the Universities and University Colleges Act 1971 and the
Constitution of the Universiti Putra Malaysia [P.U(A) 106] 15 March 1998. The Committee
recommends that the student be awarded the Master of Science
Members of the Examination Committee were as follows:
Mohd Rusli bin Yacob, PhD
Associate Professor
Faculty of Environmental Studies
Universiti Putra Malaysia
(Chairman)
Shaharin bin Ibrahim, PhD
Associate Professor
Faculty of Environmental Studies
Universiti Putra Malaysia
(Internal Examiner)
Abdul Halim bin Ghazali, PhD
Associate Professor
Faculty of Engineering
Universiti Putra Malaysia
(Internal Examiner)
Mohd Nordin bin Adlan, PhD
Professor/Ir
School of Civil Engineering
Universiti Sains Malaysia
(External Examiner)
NORITAH OMAR, PhD
Assoc. Professor and Deputy Dean
School of Graduate Studies
Universiti Putra Malaysia
Date: 19 September 2014
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This thesis was submitted to the Senate of Universiti Putra Malaysia and has been accepted as
fulfilment of the requirement for the degree of Master of Science. The members of the
Supervisory Committee were as follows:
Wan Nor Azmin Sulaiman, PhD
Professor
Faculty of Environmental Studies
Universiti Putra Malaysia
(Chairman)
Mohammad Pauzi Zakaria, PhD Professor
Faculty of Environmental Studies
Universiti Putra Malaysia
(Member)
Saim Suratman, PhD
Deputy Director
National Hydraulic Research Institute of Malaysia
(Member)
Kamaruding Samuding, PhD
Environmental Division,
Malaysian Nuclear Agency
(Member)
(BUJANG BIN KIM HUAT, PhD)
Professor and Dean
School of Graduate Studies
Universiti Putra Malaysia
Date:
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Declaration By Graduate Student
I hereby confirm that:
this thesis is my original work;
quotations, illustrations and citations have been duly referenced;
this thesis has not been submitted previously or concurrently for any other degree at
any other institutions;
intellectual property from the thesis and copyright of thesis are fully-owned by
Universiti Putra Malaysia, as according to the Universiti Putra Malaysia (Research)
Rules 2012;
written permission must be obtained from supervisor and the office of Deputy Vice-
Chancellor (Research and Innovation) before thesis is published (in the form of
written, printed or in electronic form) including books, journals, modules,
proceedings, popular writings, seminar papers, manuscripts, posters, reports, lecture
notes, learning modules or any other materials as stated in the Universiti Putra
Malaysia (Research) Rules 2012;
there is no plagiarism or data falsification/fabrication in the thesis, and scholarly
integrity is upheld as according to the Universiti Putra Malaysia (Graduate Studies)
Rules 2003 (Revision 2012-2013) and the Universiti Putra Malaysia (Research) Rules
2012.The thesis has undergone plagiarism detection software.
Signature: _______________________ Date: __________________
Name and Matric No.: ________________________________________
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Declaration by Members of Supervisory Committee
This is to confirm that:
The research conducted and the writing of this thesis was under our supervision;
Supervision responsibilities as stated in the Universiti Putra Malaysia (Graduate Studies)
Rules 2003 (Revision 2012-2013) are adhered to.
Signature; __________________ Signature; __________________
Name of Chairman
of Supervisory
Committee: __________________
Name of Member of
Supervisory
Committee: __________________
Signature; __________________
Signature; __________________
Name of Member of
Supervisory
Committee: __________________
Name of Member of
Supervisory
Committee: __________________
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TABLE OF CONTENTS
Page
ABSTRACT i
ABSTRAK iii
ACKNOWLEDGEMENTS v
APPROVAL vi
DECLARATION BY GRADUATE STUDENT viii
DECLARATION BY MEMBERS OF SUPERVISORY COMMITTEE ix
LIST OF TABLES xiii
LIST OF FIGURES xiv
LIST OF ABBREVIATIONS xvi
CHAPTER
1 INTRODUCTION 1
1.1 Background of the study 1
1.2 Problem Statement 2
1.3 Needs of the study 3
1.4 Objectives of this study 4
1.5 Scope of the study 4
1.6 Significance of the study 5
1.7 Research Framework of the study 5
1.8 Layout of the Thesis 6
2 LITERATURE REVIEW 9 2.1 Introduction 9
2.2 Concepts of Bank Infiltration 10
2.3 The History Development of Bank Infiltration 11
2.4 Factors Affecting the Siting and Design 12
2.5 The Performance of BI Systems 14
2.5.1 Attenuation Processes during BI 14
2.5.2 Contaminant Removal During BI 15
2.6 BI Limitations 18
2.7 Concept of Groundwater Flow 20
2.8 Historical Review of Modeling In BI 20
2.9 Summary 21
3 PERFORMANCE OF BANK INFILTRATION METHOD 23
3.1 Introduction 23
3.2 Study area 24
3.3 Geology 25
3.4 Methodology 25
3.4.1 Establishment of the BI site 25
3.4.2 Geophysical Investigation 27
3.4.3 Construction of Monitoring Wells and Test Wells 28
3.4.4 Sieve Analysis for Aquifer Material 28
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3.4.5 Pumping test 29
3.4.6 Stable Isotope study to identify interaction between surface 29
and groundwater
3.4.7 Groundwater Flow in the Study Site 30
3.4.8 Water Sampling and analysis 30
3.5 Results and Discussion 32
3.5.1 The BI system 32
3.5.2. Water Quality 42
3.5.3 Water Quality characteristic during BI (pumping test) 47
3.5.4 Microorganism Removal 51
3.5.5 Effectiveness and Performance of BI 51
3.6 Conclusion 55
4 MULTIVARIATE ANALYSES OF RIVER, LAKE, AND 57
GROUNDWATER INTERACTION IN BANK INFILTRATION
SITE 4.1 Introduction 57
4.2 Materials and methods 59
4.2.1 Sample Collection and Analytical Procedure 59
4.2.2 Data analyses 60
4.2.3 Discriminant Analysis (DA) 60
4.2.4 Principle Component Analysis (PCA) 61
4.3 Results and discussion 62
4.3.1 Hydrochemical Characteristics 62
4.3.2 Surface and Ground Water Classification 63
4.3.3 Surface and Groundwater Spatial Pattern Discrimination 64
4.3.4 Correlation between Variables 67
4.3.5 Source Identification Using PCA and Factor Analysis (FA) 67
4.4 Conclusion 70
5 PARTICLE TRACKING ANALYSIS OF RIVER-AQUIFER 72
INTERACTIONS VIA BANK INFILTRATION TECHNIQUES
5.1 Introduction 72
5.2 Materials and method 73
5.2.1 Conceptual model 73
5.2.2 Numerical modelling 75
5.2.3 Model parameters 76
5.2.4 Steady-state (no pump well is activated) groundwater 80
flow model and calibration
5.2.5 Transient groundwater flow simulation and calibration 81
5.2.6 Particle tracking simulation 81
5.3 Result and Discussion 82
5.3.1 Calibration Results for Groundwater Flow Simulation 82
5.3.2 Forward tracking from the river travel times and 83
pathline determination
5.3.3 Varied pumping rates and river pumping simulations 84
5.3.4 Riverbank infiltration influence zone 84
5.3.5 Backward tracking of particles: delineation of capture 85
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zone analysis
5.3.6 Mixture of groundwater, river water, and pond at the 94
pumping well
5.4 Conclusion 99
6 CONCLUSION AND RECOMMENDATIONS FOR FUTURE 101
RESEARCH 6.1 Conclusion 101
6.2 Recommendations 103
6.3 Future Research 104
REFERENCES 105
Appendices A 118
Appendices B 144
Appendices C 166
BIODATA OF STUDENTS 177
LIST OF PUBLICATIONS 178