integrated modelling for coastal alluvium aquifer at...
TRANSCRIPT
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INTEGRATED MODELLING FOR COASTAL ALLUVIUM AQUIFER AT
KG. TEKEK, TIOMAN ISLAND
LIEW KUET FAH
A project report submitted in partial fulfillment
of the requirements for the award of the degree of
Master of Engineering (Civil - Hydraulics and Hydrology)
Faculty of Civil Engineering
Universiti Teknologi Malaysia
NOVEMBER, 2006
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To my beloved parents and family
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ACKNOWLEDGEMENTS
For the accomplishment of this master project, I would like to take this
opportunity to express my deepest appreciation to my supervisor, Assoc. Prof. Dr.
Norhan Abd. Rahman, for his enthusiastic effort, suggestions, advices and guidance
during the preparation of this report. Appreciations are also dedicated to my co-
supervisor, Professor Toshiharu Kojiri of Water Resources Research Centre, D.P.R.I
Kyoto University for his willingness to comment and provide suggestions for
improvements on the results of this project.
I also gratefully acknowledge the panels of my project presentation,
consisting of Dr. Noor Baharin, Dr. Supiah Shamsudin, Ir. Ahmad Kamal and Prof.
Narayanan for their comments, opinions and suggestions to produce a better report.
I would like to extent my appreciation to my friends especially Siti, Shah,
Kamarul, Zulkifli and Hakim for their supports, cooperation and assistances during
my studies in Master program.
Last but not least, deepest thanks are expressed to my beloved parents and
family members for their moral support on my decision to further study. Without
them, I would not have been able to complete my course.
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ABSTRACT
Sufficient water supply plays an important role in busting the continuous growth of
tourism industry for an island. Tioman Island as one of the well-known marine
tourism attraction in Malaysia still highly relies on the limited surface water source
to supply water for the local residents and tourists. Thus, exploration for the
groundwater source is essential as an supplement for the existing water supply
system to cater for the increasing water demand in the future. Utilization of surface
water and groundwater will prevent the total reliance on a single resource which
avoids the water scarcity problem during drought seasons and also occurrence of
groundwater overdraft. Groundwater modellings in this study are developed with
MODFLOW2000 based on the available data to determine the hydraulic heads and
drawdowns of groundwater due to different pumping rates and saline intrusion
effects are simulated with the SEAWAT2000 model. The linear optimization
problem is solved with GAMS to maximize the rate of pumping for groundwater to
fulfill the quantity and quality requirements. The aquifer system would be capable to
support withdrawal of groundwater up to 5.8 MLD and cater for water demand till
year 2015. The hydraulic drawdown has greater influence for the optimization of
pumping rate compared to saline intrusion effects. With additional supply from
surface water source of 4 MLD, the combination system could cater for the water
demand up to year 2025.
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ABSTRAK
Bekalan air yang mencukupi memainkan peranan penting bagi perkembangan
industri perlancongan yang berterusan di sebuah pulau. Pulau Tioman sebagai salah
satu tumpuan perlancongan marin yang terkenal di Malaysia masih bergantung
kepada sumber air permukaan yang terhad untuk membekalkan air kepada penduduk
tempatan dan pelancong. Dengan itu, penerokaan sumber air bumi adalah penting
sebagai sumber tambahan bagi sistem bekalan air yang sedia ada untuk menampung
keperluan air yang semakin meningkat pada masa depan. Penggunaan air permukaan
and air bumi akan mengelakkan masalah kekurangan air pada musim kemarau dan
berlakunya pengepaman air bumi yang berlebihan. Model MODFLOW2000 telah
digunakan dalam kajian ini untuk membentuk model simulasi berdasarkan kepada
data yang sedia ada untuk menentukan turus hidraulik air bumi disebabkan oleh
pengepaman pada kadar alir yang berbeza. Model SEAWAT2000 pula menganalisa
kesan pencerobohan air masin pada setiap kadar pengepaman. Masalah penyelesaian
linear diselesaikan dengan GAMS untuk memperolehi kadar pengepaman yang
maksimum dan memuaskan syarat kuantiti dan kuality. Hasil kajian menunjukan
sistem akuifer mampu mengeluarkan air bumi sebanyak 5.8 MLD dan menampung
keperluan air sehingga tahun 2015. Penurunan turus hidraulik menunjukkan
pengaruh yang lebih besar berbanding dengan pencerobohan air masin dalam proses
mengoptimumkan kadar pengepaman. Dengan bekalan tambahan sebanyak 4 MLD
daripada sumber air permukaan, sistem kombinasi dapat menampung bekalan air
sehingga tahun 2025.
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TABLE OF CONTENTS
CONTENTS PAGE
DECLARATION OF ORIGINALITY AND EXCLUSIVENESS ii
DEDICATION iii
ACKNOWLEDGEMENT iv
ABSTRACT v
ABSTRAK vi
CONTENTS vii
LIST OF TABLES xi
LIST OF FIGURES xii
LIST OF APPENDICES xv
CHAPTER 1 INTRODUCTION 1
1.1 Background of the study 1
1.2 Objectives of study 2
1.3 Scope of study 3
1.4 Importance of study 3
CHAPTER 2 LITERATURE REVIEW 5
2.1 Groundwater Hydrology 5
2.1.1 Groundwater and Hydrologic Cycle 5
2.1.2 Groundwater Movement 7
2.1.3 Groundwater Recharge and Discharge 8
2.1.4 Aquifer and Confining Beds 8
2.2 Groundwater Quality 10
2.2.1 Saline Intrusion in Coastal Zones 11
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2.3 Type of Groundwater Models 13
2.4 Historical Review of Groundwater Modelling
in Malaysia 15
2.4.1 Historical Review of Groundwater
Modelling in Kelantan 15
2.4.2 Historical Review of Previous Studies of
Alluvial Aquifer in Tioman Island 17
2.5 Historical Review of MODFLOW and SEAWAT
Application for Tymbaki Aquifer, South Central
Crete, Greece (2005) 20
2.5.1 Site Description and Basin Hydrogeology 21
2.5.2 Simulation Models 23
2.5.3 Discretization, Boundary Condition and
Aquifer Parameters 23
2.5.4 Simulation Results and Conclusion 25
2.6 Optimization Modelling 27
2.6.1 Linear Programming 28
2.7 Historical Review of GAMS Application for
Groundwater Management in the Goksu Delta
At Silifke, Turkey (2001) 30
2.7.1 Objective Function and Constraints 31
2.7.2 Results and Discussion 34
2.8 Summary 36
CHAPTER 3 METHODOLOGY AND STUDY AREA 37
3.1 Modelling of Groundwater and Optimization 37
3.2 Description of the study area 37
3.2.1 Geology and Hydrogeology 42
3.2.2 Climate 44
3.2.3 Topography 44
3.2.4 Water Resources of Study Area 46
3.2.5 Hydrology 46
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3.3 Groundwater Modelling 46
3.3.1 MODFLOW2000 47
3.3.1.1 Spatial and Time Discretization 49
3.3.1.2 Governing Equation 50
3.3.2 SEAWAT2000 51
3.3.2.1 Temporal Discretization 53
3.3.2.2 Head and Equivalent Freshwater 54
Head in SEAWAT2000
3.3.2.3 Variable-Density Groundwater 55
Flow Equation
3.4 Simulation Setup 56
3.4.1 Simulation Time Steps 58
3.4.2 Boundary Condition 58
3.4.3 Data Input Parameters 58
3.4.4 Model Assumptions 59
3.5 Optimization Model 59
3.5.1 General Algebraic Modeling Systems
(GAMS) 60
3.5.2 Objective Function 60
3.5.3 Constraints 60
3.5.4 Water Consumption Projection 63
3.6 Integrated Modelling Approach 63
CHAPTER 4 RESULTS, ANALYSIS AND DISCUSSIONS 66
4.1 Introduction 66
4.2 Simulation Results for MODFLOW2000 67
4.2.1 Calibration Process 67
4.2.2 Simulation Analysis 70
4.3 Simulation Results for SEAWAT2000 79
4.3.1 Calibration and Validation Process 79
4.3.2 Simulation Analysis 81
4.4 Optimization Results 94
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CHAPTER 5 CONCLUSIONS AND RECOMMENDATIONS 97
5.1 Conclusions 97
5.2 Recommendations 98
REFERENCES 99
APPENDICES 102
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LIST OF TABLES
TABLE NO. TITLE PAGE
2.1 Application of groundwater modelling at
Tioman Island 20
2.2 The calibrated model parameters 24
2.3 Application of groundwater management and
Optimization modelling in coastal aquifer of Malaysia 28
3.1 Processes and Packages of MODFLOW-2000 48
3.2 Projected water consumption for Kg. Tekek 63
4.1 Values for constant parameters 67
4.2 Cases considered for the calibration process 68
4.3 Calibration analysis results for Case (1) 69
4.4 Calibration analysis results for Case (2) 70
4.5 The aquifer influence coefficients of drawdown
for TEK1 76
4.6 Calibration results for SEAWAT2000 80
4.7 Validation results for SEAWAT2000 80
4.8 Calibrated parameters for SEAWAT2000 model 81
4.9 Optimization results for pumping well TEK1 95
4.10 Water supply for combine system 96
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LIST OF FIGURES
FIGURE NO. TITLE PAGE
1.1 Location of Tioman Island 4
2.1 Hydrological Cycle 6
2.2 Flow paths associated with local, intermediate
and regional flow systems 7
2.3 The aquifer and the confining beds 9
2.4 Saltwater intrusion occurrence due to pumping well 12
2.5 Location map of the Tymbaki and Mesara basin 21
2.6 Geological map of Tymbaki basin 22
2.7 Geological cross section of Tymbaki basin 22
2.8 Rainfall and streamflow infiltration recharge zone 25
2.9 Simulated extent of seawater intrusion into the
Tymbaki aquifer at various depth 26
2.10 Seawater intrusion along section C1 at the end of
120th stress period 26
2.11 Seawater intrusion along section C1 at the end of
240th stress period 26
2.12 The Goksu Delta 31
2.13 Correlation between simulation model results and
optimization model results for hydraulic heads 34
2.14 Correlation between simulation model results and
optimization model results for chloride concentrations 35
2.15 Trade-off curves between maximum pumping rate
and chloride concentration limit 35
3.1 Groundwater simulation and optimization model
for the study 38
3.2 Methodology Flow Chart 39
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3.3 Groundwater modelling process flow chart 40
3.4 Location of Kg. Tekek in Tioman Island 41
3.5 Geologic map for Tioman Island 42
3.6 Geological cross section for Kg. Tekek aquifer system 43
3.7 Topography map for Tioman Island 45
3.8 Finite difference grid 50
3.9 Simulation modes available with the
SEAWAT2000 programme 53
3.10 Horizontal plane and vertical section of the
Groundwater models 57
3.11 Input and output for integrated modelling 65
4.1 Hydraulic conductivity zoning plan for
Kg. Tekek (isotropic heterogeneous) 68
4.2 Location of pumping wells at Kg. Tekek 69
4.3 Hydraulic head contour due to pumping of 1 MLD 71
4.4 Hydraulic head contour due to pumping of 2 MLD 72
4.5 Hydraulic head contour due to pumping of 3 MLD 73
4.6 Hydraulic head contour due to pumping of 4 MLD 74
4.7 Hydraulic head contour due to pumping of 5 MLD 75
4.8 Hydraulic head at TEK1 77
4.9 Hydraulic head at TEK3 and TEK4 78
4.10 Relationship between hydraulic drawdown
and pumping rate at TEK1 79
4.11 Concentration contour (saline intrusion) on
horizontal plane due to pumping of 0.5 MLD 82
4.12 Concentration contour (saline intrusion) on
vertical section due to pumping of 0.5 MLD 83
4.13 Concentration contour (saline intrusion) on
horizontal plane due to pumping of 1 MLD 84
4.14 Concentration contour (saline intrusion) on
vertical section due to pumping of 1 MLD 85
4.15 Concentration contour (saline intrusion) on
horizontal plane due to pumping of 1.5 MLD 86
4.16 Concentration contour (saline intrusion) on
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vertical section due to pumping of 1.5 MLD 87
4.17 Concentration contour (saline intrusion) on
horizontal plane due to pumping of 2 MLD 88
4.18 Concentration contour (saline intrusion) on
vertical section due to pumping of 2 MLD 89
4.19 Concentration contour (saline intrusion) on
horizontal plane due to pumping of 2.5 MLD 90
4.20 Concentration contour (saline intrusion) on
vertical section due to pumping of 2.5 MLD 91
4.21 Concentration contour (saline intrusion) on
horizontal plane due to pumping of 3 MLD 92
4.22 Concentration contour (saline intrusion) on
vertical section due to pumping of 3 MLD 93
4.23 Relationship between saline intrusion length
and pumping rate 94
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LIST OF APPENDICES
APPENDIX PAGE
A1 Analysis results of groundwater in Kg Tekek 103
(source : ALS Technichem (M) Sdn. Bhd. 28 March 2003)
A2 Analysis results of groundwater in Kg. Tekek 104
(source : ALS Technichem (M) Sdn. Bhd. 28 March 2003)
(continue)
A3 Analysis results of groundwater in Kg. Tekek 105
(source : FELDA AGRICULTURAL SERVICES SDN. BHD.
8 July 2004)
A4 Analysis results of groundwater in Kg. Tekek
106
(source : FELDA AGRICULTURAL SERVICES SDN. BHD.
8 July 2004)(continue)
A5 Water Quality Monitoring (6 June- 7 June 2004)
107
by Universiti Teknologi Malaysia
A6 Water Quality Result During Pumping Test In Kg. Tekek 108
by Universiti Teknologi Malaysia
A7 Water Quality Result During Pumping Test In Kg. Tekek 109
by Universiti Teknologi Malaysia. (continue)
A8 Analysis results of groundwater in Kg Tekek 110
(source : ALS Technichem (M) Sdn. Bhd. 31 December 2003)
A9 Analysis results of groundwater in Kg. Tekek 111
(source : ALS Technichem (M) Sdn. Bhd. 31 December 2003)
A10 Analysis results of groundwater in Kg. Tekek 112
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(source : ALS Technichem (M) Sdn. Bhd. 31 December 2003)
A11 Analysis results of groundwater in Kg. Tekek 113
(source : ALS Technichem (M) Sdn. Bhd. 31 December 2003)
A12 Analysis results of groundwater at various depths in Kg. Tekek 114
(source : Department of Environment 2001 - 2005)
A13 Analysis results of groundwater at various depths in Kg. Tekek 115
(source : Department of Environment 2001 - 2005)
B1 Constant Discharge Pump Test Record (Tek 1) 116
B2 Constant Discharge Pump Test Record (Tek 3) 117
B3 Constant Discharge Pump Test Record (Tek 4) 118
B4 Recovery Test (Tek 1) 119
B5 Recovery Test (Tek 3) 120
B6 Recovery Test (Tek 4) 121
B7 Recovery Test (Piez 7) 122
B8 Constant Discharge Pump Test Record (Piez 1) 123
B9 Constant Discharge Pump Test Record (Piez 2) 124
B10 Constant Discharge Pump Test Record (Piez 3) 125
B11 Constant Discharge Pump Test Record (Piez 4) 126
B12 Constant Discharge Pump Test Record (Piez 5) 127
B13 Constant Discharge Pump Test Record (Piez 6) 128
B14 Constant Discharge Pump Test Record (Piez 7) 129
C Optimization Model 130 - 132
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CHAPTER 1
INTRODUCTION
1.1 Background of the Study
Tioman Island, as one of the marine tourism destination in Malaysia, is
located in the South China Sea, 56 km off Mersing. The island having a total area of
about 131 km2, spanning about 11 km from west to east and 20 km from north to
south, is the largest among a group of 64 volcanic islands in the South China Sea.
Noted for its crystal clear water and marine life, the island in the vicinity of 2°43’00”
to 2°54’00” N latitude and 104°06’00” to 104°12’30” E longitude, have attracted
many tourists both local and abroad annually. In addition to fishing activities,
tourism has become a very important income generating activity on the island.
Due to the importance of water as the basic criteria for the development of
tourism, many studies have been carried out to determine the water availability on
the island. Based on this purpose of study, Nazan Awang (1988) had suggested Kg.
Tekek and Kg. Juara to be the potential areas for surface water and groundwater
extraction on the island. The study also explored into annual water yield from surface
as well as groundwater sources in Kg. Tekek by using simulation model based on the
site collected data.
Presently, the limited availability of surface water sourced from the river
system serves as the main source of water supply in the vicinity for domestic and
tourism demands. Groundwater utilization is only available in certain parts of the
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area on the island in the form of individual wells. Groundwater system for public
water supply is still virtually non-existent. The government’s intention to promote
Tioman Island as a tax-free tourist based island will further burden the water stress.
Thus exploration for new reliable water sources is essential to cater for the increasing
water demand due to population and tourist growth.
The extraction of available groundwater will be the best solution for the water
crisis problem on Tioman Island other than water transfer from the mainland. The
main concern for groundwater aquifer to be developed as public water supply will be
the maximum yield available. Pumping of groundwater may cause deleterious side
effects if proper management and water conservation aspects are neglected. For
coastal aquifer system, water quality degradation due to saline intrusion effects may
limit the application of groundwater, therefore careful study should be carried out on
groundwater aquifer to ensure a sustainable water supply of the area.
1.2 Objectives of Study
The objectives of this study include:
a. To predict the available yield of the groundwater flow system due to different
pumping rate on Tioman Island.
b. To study the saline intrusion effects under different pumping rate.
c. To study the maximum pumping rate of groundwater for optimization.
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1.3 Scope of Study
The study on groundwater aquifer system at Tioman Island involves scopes
as listed below:
a. The study will focus on the groundwater system in Kg. Tekek, Tioman Island
(Figure 1.1).
b. The simulation process involves groundwater numerical models, which
include MODFLOW for groundwater flow and SEAWAT for saline intrusion
effects.
c. The optimization of pumping rate that involves application of simulated
results into linear programming for GAMS.
1.4 Importance of Study
As the basic human need, water is an essential criterion that enables the
continuous growth in tourism industry of Tioman Island. The analytical data in 1999
provided by Hassan indicated that the surface runoff is limited and inconsistent, with
fluctuating water amount following the annual climatic changes. In order to ensure
continuous availability of water supply to local residents and tourists, alternative
water sources will be required to supplement or replace diminished surface water
supplies. Groundwater resources available in several areas on the island will be a
potential option to the solution of the crisis, but extensive studies are still required to
determine the advantages and disadvantages of implementation.
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Figure 1.1: Location of Tioman Island.
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REFERENCES
Christian D. Langevin (2001). “Simulation ater Discharge to Biscayne
Bay, Southeastern Florida.” U.S. Geological Survey, Water-Resources
Investigation Report 00-4251.
Christian D. Langevin, Eric D. Swain, Harry L. Jenter and Raymond W. Schaffranek
(2001). “The Tides and Inflows in the Mangroves of the Everglades Project.”
Florida Bay Science Conference, Key Largo, Florida, 23 – 26 April.
Christian Langevin, Eric Swain, Melinda Wolfert (2004). “Simulation of Integrated
Surface-Water/Ground-Water Flow and Salinity for a Coastal Wetland and
Adjacent Estuary.” Journal of Hydrology 314, pg. 212-234
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