i POLLUTION MONITORING AT SUNGAI SEMANTAN...
Transcript of i POLLUTION MONITORING AT SUNGAI SEMANTAN...
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POLLUTION MONITORING AT SUNGAI SEMANTAN TRIBUTARIES USING
GEORAPHICAL INFORMATION SYSTEM
NORIKA BINTI KARIM
A project report submitted in partial fulfilment of the
requirements for the award of the degree of
Master of Engineering (Civil)
Faculty of Civil Engineering
Universiti Teknologi Malaysia
JUNE 2017
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DEDICATION
Dedicated to Allah S.W.T,
my beloved husband Amron Bin Sawat
and my lovely childrens,
Nur Alya Syahirah , Muhammad Alif Safwan, Muhammad Alif Syazani
Muhammad Alif Syazwi, Muhammad Alif Firdaus and Muhammad Alif Fateh
Thanks for your valuable sacrifice and love.
To my beloved parents,
Karim Bin Hassan – Norisah Binti Abd Hamid
Rubiah Binti Kardi.
Thanks for your support and always being there for me in happiness and sadness.
~~~~~ Love you all ~~~~~
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ACKNOWLEDGEMENT
I would like to thank Allah S.W.T for blessing me with excellent health and ability
during the process of completing my thesis. Special thanks to my supervisor Professor
Madya. Dr. Johan Bin Sohaili who have given me the opportunity to learn a great deal
knowledge, and guiding me towards fulfilling this achievement.
My gratitude is also extended to the staff in Jabatan Pengurusan Air Pahang Berhad
which gives guide during the laboratory analysis in Mempaga Water Treatment Plant,
Bentong. Thank you for the support and friendship showered upon me throughout the
experimental periods.
I would like to thank my master studies colleagues and staff at Geomatic of Civil
Engineering Department in Politeknik Sultan Haji Ahmad Shah for their support.
Finally, I would like to thank my lovely husband Amron Bin Sawat for his
unconditional support and assistance in various occasions. All your kindness will not be
forgotten.
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ABSTRACT
The availability of fresh water for human use has become a problem due to
climate change scenario. This study aims to assess the water quality patterns of
pollution concentrations in Sungai Semantan catchment using GIS. This spatial
pattern of each parameter was then analysed based on the Water Quality Index
(WQI) and National Water Quality Standards (NWQS) to determine the locations of
major pollutant sources that contribute to water quality depletion in the Sungai
Semantan catchment. The considerations of sampling were focused on land use data
that contributes to high potential impact to water quality. The water sampling was
collected from nine different locations of the Bentong region starting from Sungai
Bentong and Sungai Kelau to Sungai Semantan in the sunny and rainy seasons from
November 2016 to April 2017. The samples collected were then analysed for
different physicochemical parameters including pH, TSS, DO, BOD, COD, NH3-N,
turbidity, colour, iron and manganese to determine the spatial distribution of water
quality in the study area. Geo-statistical analysis and Geographical Information
System (GIS) were used to visualize the spatial pollution characteristics and identify
potential polluted risky regions. From the obtained results of the parameters
characteristics, it can be concluded that the water in Sungai Semantan is disturbed
due to the presence of BOD, COD, TSS, turbidity, colour, iron and manganese
concentrations. This parameter was exposed to various pollutants and seriously
exceeded the standard of Category III (refer Malaysia NWQS). However, based on
WQI, most of the parameters measured remained in Class II ranged from 85.12 to
90.11 (mean 88.13). In this study, the final representation of WQI has been done on
the GIS map to show the spatial variation of pollution levels in the entire Sungai
Semantan catchment. It is suggested that monitoring should be carried out
continuously for proper management of this river basin to ensure sustainability of the
water supply. WQI calculation formula should be reviewed by authorities to ensure
important water quality parameter is relevant to analysis.
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ABSTRAK
Perubahan iklim yang berlaku hari ini menjadi masalah utama kepada negara
terhadap kecukupan bekalan air kepada masyarakat sejagat. Kajian ini bertujuan
membuat penilaian kepada pencemaran corak kualiti air di kawasan tadahan di
Sungai Semantan menggunakan GIS. Corak spatial setiap parameter yang telah
dianalisis kemudian dikelaskan berdasarkan Indeks Kualiti Air (WQI) dan Piawaian
Kualiti Air Kebangsaan (NWQS) untuk menentukan parameter pencemaran air yang
utama menyebabkan mutu air di Sungai Semantan terjejas. Persampelan memberi
tumpuan kepada faktor guna tanah yang menyumbang kepada potensi yang tinggi
untuk memberi kesan kepada kualiti air. Persampelan diambil di 9 lokasi yang
berbeza bermula dari Sungai Bentong dan Sungai Kelau ke Sungai Semantan di
musim yang cerah dan hujan dari November 2016 hingga April 2017. Sampel
kemudian dianalisis menggunakan sepuluh parameter merangkumi ciri-ciri fizikal
dan kimia iaitu pH, TSS, DO, BOD, COD, NH3-N, kekeruhan, warna, besi dan
mangan untuk menentukan taburan spatial kualiti air di kawasan kajian. Analisis
statistik dan Sistem Maklumat Geografi (GIS) telah digunakan untuk
menggambarkan ciri-ciri dan potensi taburan pencemaran kawasan tercemar yang
berisiko tinggi. Hasil dari analisis, dapat disimpulkan air di Sungai Semantan
terganggu kerana kehadiran BOD, COD, TSS, kekeruhan, warna, besi dan mangan.
Parameter ini didedahkan dengan pelbagai pencemaran melebihi kelas Kategori III
merujuk kepada (NWQS). Walau bagaimanapun, WQI adalah berdasarkan parameter
yang diukur kekal di dalam kelas II antara 85.12 – 90.11 (min 88.13). Dalam kajian
ini, taburan WQI telah dilakukan menggunakan GIS menggunakan kaedah Kriging
untuk menunjukkan perubahan tahap pencemaran keseluruhan kawasan tadahan di
Sungai Semantan. Di harap pihak yang bertanggungjawab dapat menjalankan
pemantauan berterusan bagi memastikan lembangan sungai ini terus kekal bersih
bagi memastikan kemampanan bekalan berkekalan.
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TABLE OF CONTENTS
CHAPTER TITLE PAGE
DECLARATION ii
DEDICATION iii
ACKNOWLEDGEMENT iv
ABSTRACT v
ABSTRAK vi
TABLE OF CONTENTS vii
LIST OF TABLES x
LIST OF FIGURES xi
LIST OF APPENDICES xiv
LIST OF SYMBOLS AND ABBREVIATIONS xv
1
INTRODUCTION
1
1.1 Introduction 1
1.2 Problem of Statement 2
1.3 Background of Study 4
1.4 Aim and Objectives 5
1.5 Scope of Study 6
1.6 Significance of Study 6
2
LITERATURE REVIEW
7
2.1 Introduction 7
2.2 Nonpoint Sources (NPS) 9
2.3 Point Sources 10
2.4 Water Quality Assessment 11
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2.4.1 Water Quality Index 12
2.4.2 WQI Formula and Calculation 15
2.5 Pollution Load 16
2.5.1 Biochemical Oxygen Demand Load 17
2.5.2 Total Suspended Solids 18
2.5.3 Ammoniacal Nitrogen Load 20
2.5.4 Dissolve Oxygen 22
2.5.5 Chemical Oxygen Demand 23
2.5.6 Turbidity 23
2.5.7 Iron 24
2.5.8 Manganese 24
2.5.9 Colour 25
2.6 GIS Water Quality Information System 25
2.7 GIS Mapping Procedure 26
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METHODOLOGY 28
3.1 Introduction 28
3.2 Research Frame Work 29
3.3 Site Description 30
3.4 Sampling Sites 32
3.5 Laboratory Analysis 34
3.6 Data Evaluation 35
3.6.1 Water Quality Parameter 36
3.6.2 Digital Elevation Model 36
3.6.3 Land Use 39
3.7 Model Development Using ArcGIS 40
3.8 Map Projection 41
3.8.1 Water Quality Interpolation 42
4
ANALYSIS DATA
45
4.1 Introduction 45
4.2 Water Quality Variation 45
4.2.1 Temperature 46
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4.2.2 pH 48
4.2.3 Dissolved Oxygen 50
4.2.4 Biochemical Oxygen Demand 52
4.2.5 Chemical Oxygen Demand 54
4.2.6 Ammoniacal Nitrogen 56
4.2.7 Total Suspended Solid 58
4.2.8 Turbidity 60
4.2.9 Colour 62
4.2.10 Iron 64
4.2.11 Manganese 66
4.3 Summary of Water Quality Parameter 69
4.4 Water Quality Index 70
4.4.1 Sub- Indexes of Water Quality
Parameters 70
4.4.2 Water Quality Index 71
4.5 General Discussion 75
4.5.1 The factor of pollution concentration 78
5
CONCLUSION 80
5.1 Introduction 80
5.2 Recommendations 82
5.3 Areas for Further Research 83
REFERENCES 85
Appendices A -B 89 -94
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LIST OF TABLES
TABLE NO. TITLE PAGE
2.1
National Water Quality Standards (NWQS) for
Malaysia 13
2.2 Water classes and uses according to WQI 13
2.3
Water Quality Classification Based On Water Quality 14
Index
2.4 Classification of Water Quality Index 14
2.5 DOE-WQI calculation formula 16
2.6 Particle Sizes Found in Water Treatment 18
3.1 The GPS Coordinates of the sampling stations. 33
3.2 Water Quality Parameters, Standard and Equipment 34
3.3 Type and Source of Data Used 35
3.4 Feature Class 42
4.1
Statistical summary of water quality parameter 69
properties on Sunny Season.
4.2 Statistical summary of water quality parameter properties on Rainy Season. 69
4.3 Sub-Indexes of water quality parameters for different water sampling stations. 71
4.4 Water quality status and WQI at sampling stations in
Sungai Semantan watershed 72
4.5 Statistical summary of water quality parameter properties on sunny season and rainy season 77
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LIST OF FIGURES
FIGURE NO. TITLE PAGE
2.1 Location of Bentung in Malaysia 8
2.2 Biochemical Oxygen Demand (BOD5 ) load in 2014. 17
2.3 Suspended Solids (SS) load in 2014 19
2.4 Example of organic and inorganic particles which
contribute to the suspended solid concentration 20
2.5 Ammoniacal Nitrogen (NH3-) load in 2014 22
2.6 GIS Mapping procedure for Water Quality Data 27
3.1 A Flowchart to conduct a Study 29
3.2 Study Location 30
3.3 Sungai Kelau and Sungai Bentong which located near forest and built up land respectively 30
3.4 The pam house Pahang Selangor Raw Water Transfer
located in Sungai Semantan 31
3.5 Boundary Sungai Semantan Catchments 31
3.6 Location of Selected Station 32
3.7 Topography study area to produce DEM. 37
3.8 DEM from SRTM satellite 38
3.9 The DEM of Bentong and Temerloh 38
3.10 Land use Map of Study Area 39
3.11 Geostatistical Analyst using ArcGIS 10.1 Desktop 41
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3.12 Coordinates mapping using RSO in the real-world
coordinate 41
3.13 The table of Mean Water Quality Created in Excel 43
3.14 Location of water quality station 43
3.15 Location of river with station 43
3.16 Result of the Kriging process 44
3.17 Spatial distribution pattern of water quality 44 parameter
4.1 Temperature variation. A) Sunny Season B) Rainy Season 47
4.2 Temperature at sampling stations. A) Sungai
Bentong B) Sungai Kelau 47
4.3 Spatial Distribution of PH value. A) Sunny Season B) Rainy Season 49
4.4 Concentration of pH. A) Sungai Bentong B) Sungai Kelau 49
4.5 Spatial Distribution of DO value. A) Sunny Season B) Rainy Season 51
4.6 Concentration of DO. A) Sungai Bentong B) Sungai
Kelau 51
4.7 Spatial Distribution of BOD value. A) Sunny Season 53
B) Rainy Season 51
4.8 Concentration of BOD. A) Sungai Bentong B) Sungai Kelau 54
4.9 Spatial Distribution of COD value in Sunny Season 55
4.10 Concentration of COD. A) Sungai Bentong B) Sungai 56
Kelau 54
4.11
Spatial Distribution of NH3-N value. A) Sunny
Season B) Rainy Season 57
4.12 Concentration of Amoniacal Nitrogen at sampling 58
station A) Sungai Bentong B) Sungai Kelau
4.13 Spatial Distribution. A) Sunny Season B) Rainy Season 59
4.14 Concentration of Suspended Solid at sampling
stations. A) Sungai Bentong B) Sungai Kelau 60
4.15 Spatial Distribution of Turbidity value. A) Sunny
Season B) Rainy Season 61
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4.16 Concentration of Turbidity. A) Sungai Bentong B) Sungai Kelau 62
4.17 Spatial Distribution of Colour value. A) Sunny Season B) Rainy Season 63
4.18 Concentration of Colour. A) Sungai Bentong
B) Sungai Kelau 64
4.19 Spatial Distribution of Iron value. A) Sunny Season 65
B) Rainy Season 63
4.20 Concentration of Iron. A) Sungai Bentong B) Sungai Kelau 64
4.21 Spatial Distribution of Manganese value. A) Sunny Season B) Rainy Season 67
4.22 Concentration of Manganese at sampling stations. A) Sungai Bentong B) Sungai Kelau 68
4.23 Concentration of water quality parameters at sampling stations 70
4.24 Spatial distribution of Water Quality Index
B) Sungai Kelau 73
4.25 WQI of designated locations along Sungai Semantan. A) Sungai Bentong B) Sungai Kelau 73
4.26 Land clearance for agriculture will increase turbidity, total suspended solid and colour in water. 76
4.27 Affected area in water treatment plant for water 76 supply
4.21 Spatial Distribution of Manganese value. A) Sunny Season B) Rainy Season 67
4.22 Concentration of Manganese at sampling stations. A) Sungai Bentong B) Sungai Kelau 68
4.23 Concentration of water quality parameters at sampling stations 70
4.24 Spatial distribution of Water Quality Index B) Sungai Kelau 73
4.25 WQI of designated locations along Sungai Semantan.
A) Sungai Bentong B) Sungai Kelau 73
4.26 Land clearance for agriculture will increase 76
4.27 Affected area in water treatment plant water supply
76
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LIST OF APPENDICES
APPENDIX TITLE PAGE
A Sampling Station 90
B Water QualityParameter 91
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LIST OF SYMBOLS AND ABBREVIATIONS
BOD - Biochemical Oxygen Demand
COD - Chemical Oxygen Demand
DO - Dissolved Oxygen
TSS - Total Suspended Solid
NH3-N - Ammoniacal Nitrogen
Fe - Iron
TDS - Total Dissolved Solids
TH - Total Hardness
EC - Electrical Conductivity
Mn - Manganese
WQI - Water Quality Indexs
NWQS - National Water Quality Standards for Malaysia
GIS - Geografical Information System
DEM - Digital Elevation Model
GPS - Global Positioning System
% - Percentage
°C - Degree Celcius
1
CHAPTER 1
INTRODUCTION
1.1 Introduction
Water is one of the most important substances on humans life. All humans,
plants and animals must have water to survive. If there is no water in the world,
there would be no life cycle on earth. Besides drinking to survive, humans use water
for cooking, washing clothes, keeping houses and communities clean and keeping
plants alive in gardens and parks. Water is necessary for all living organisms. The
quality of water is getting progressively worse as a result of the pollution from
industrialisation, agriculture, mining, burning, land ownership and forestation. This
affects the health and socioeconomics of the region.
Malakootian et al. (2010) observed that the presence of colour in water
effects the consumer assurance toward the quality of drinking water. People
atheistically do not accept coloured and odour water. Water with high amount of
colour and odour is not suitable for clothes washing and dyeing, paper industry,
beverages production, dairies and other food products, the textile industry, as well as
plastic production.
Water quality monitoring gives an idea about the extent of deterioration
caused by this essential requirement. Water quality data is usually represented in
tables and graphs. As the number of sampling stations and parameters to be analysed
increases, the difficulty for analysing the data and interpretation of parameters that
affect water quality increases. The visual results for water quality monitoring helps
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to give a clearer picture of the water quality for river water. This can be achieved by
using Geographic Information System (GIS).
GIS is applied in various fields such as agriculture, business, geography,
defence and intelligence, ecology and conservation, emergency management and
public safety, environmental management, forestry, health care, education, mining
and geosciences, oceanography, coastal zone, marine resources, remote sensing and
imagery, state and local government, telecommunications, transportation and water
distribution and resources. GIS can effectively be used for water quality
management. Spatially referenced data concerning water pollution can be employed,
stored and displayed using GIS. Overlaying techniques is a useful tool with digital
data layers.
Water quality analysis is important to understand the wealth of living
organisms and environmental conditions in water bodies. Nagalakshmi et al. (2016)
applied the ordinary Kriging interpolation method for surface analysis of water
quality parameter for analysing the dispersion patterns.
The spatial distribution of water pollutants and other water quality parameters
can be displayed effectively using GIS. This will helps authorities in taking effective
actions to monitor the water quality that can reduce water pollution.
1.2 Problem of Statement
Water pollution is a serious environmental problem to humans’ and animals’
health. Saher et al.(2012) has studied pollution monitoring along the Pahang river
basin and have been concluded that the most effective approach for water quality
protection in a watershed is to monitor the source of pollution and make
improvements and implementation plans to reduce or mitigate those critical sources.
The Pahang-Selangor Raw Water Transfer (PSWT) has now completely and fully
transferred water to the Selangor state.
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This study will focus on the contribution of point and non-point sources of
pollution using upstream – downstream sampling sites. The PSWT station located at
Sungai Semantan collects water from Sungai Bentong (54.5km) and Sungai Kelau
(21km) that is expected to have a synergistic effect on the water quality of the river.
According to the New Straits Times, Oct 12, the Pahang Department of Environment
(DOE) is prepared to meet with the Selangor state government to discuss claims
about water pollution at Sungai Semantan, Bentong. The pollution contributes to the
closure of the Langat and Cheras water treatment plants. The water from Sungai
Semantan in Bentong transferred to the Langat and Cheras water treatment plants
(LRA) in Selangor is assumed to contain chemical and hazardous waste. The water
tunnel is being built as part of the PSWT project aimed to supply raw water from
Sungai Semantan to the states of Pahang, Selangor, Kuala Lumpur and Negeri
Sembilan. Water from the tunnel will be supplied using 858m long inlet conduit
structure and the pumping station located in the Pahang River Catchment. The outlet
structure in Selangor will transfer the water to the Langat and Cheras treatment plant.
The DOE has a monitoring programme that focuses on upstream and
downstream in the affected area. The focus is mainly on point source. Maimon and
Zainudin (2013) stated that rivers are mainly polluted due to the point and non-point
pollution sources. Point sources are monitored and controlled by the DOE, whereas
a significant amount of pollutants are contributed by both untreated sullage and
storm runoff.
However, because of the presence point and non-point sources of pollution in
the catchment area, the need to conduct an integrated assessment of the possible
impacts on the river water quality is justified. Therefore, using the development of
technologies, GIS modelling can be useful to analyse the data obtained.
Oke and Ogedengbe (2013) mentioned that GIS is actuality recognised as a
powerful tool to overcome the issues and manage the geographical information in a
universal method without losing the spatial historical variability which is often
critical in monitoring and decision making. Furthermore, Kadhem (2013) also has
used GIS in order to compare the water quality parameter and related information
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collected from the Tigris River, displaying the distribution concentration of the river
in easily viewed maps.
1.3 Background of Study
According to a report from the Department of Environmental Malaysia
(DOE, 2015), the sources of water pollution can be considered into point and non-
point sources. Point sources are referred to as sources with discharges entering the
body of water at a specific location such as from pipes or outfalls. Point sources
include the discharges from industries, sewage treatment plants and animal farms.
Non-point sources are derived from diffuse sources that do not have a specific
discharge point; examples of which are from agricultural activities.
Furthermore, Gyrson et al. (2012) stated that water colour is the problem
faced by UK water companies which takes raw water from peatland catchments. A
water colour model has been developed using a combined GIS and Multicriteria
Evaluation approach. The model developed was then used to predict water colour
production potential based on key land management practices to control colour
production in UK upland catchments.
Based on research studies by Saher et al. (2012), the required datasets were
generated using remote sensing and GIS system integrated with field GPS surveys.
The representations of these datasets are an advanced method to ensure the data
quality and output results. The study was to find out the Pahang River pollution and
environmental threats by assessing and analysing different data layers of
topographical, geological, hydrological and land cover using GIS method.
Besides that, Othman et al. (2011) mentioned that computer models are used
extensively for the water-quality management of rivers and streams. These models
must usually be calibrated to adjust a large number of parameters to reach the
optimal agreement between model output and field measurements.
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1.4 Aim and Objectives
The objective of this research is related to a set of aims or targets to be
achieved through the completion of the research. The main objective of the study
was to:-
i. To develop a map capable of predicting the patterns of pollution
concentrations of the Sungai Semantan catchment.
ii. To evaluate the variation different of water quality on the contribution of
point sources and non-point sources along the river for measuring
changes of water quality.
iii. To construct the water quality of Sungai Semantan based on Interim
National Water Quality Standard (INWQS) and Water Quality Indexes
(WQI).
1.5 Scope of Study
The scope of work covers the chemical and physical characteristics of water
quality using the National Water Quality Standard (NWQS) in Malaysia and WQI.
This study was focused on collecting data from the sampling point. Ten (10)
physical and chemical parameters were monitored to provide the baseline
information on the water quality status of the rivers in the Sungai Semantan
catchments.
The following are information about the data that shall be finalised:
i. Water Quality Data – pH, Dissolve Oxygen (DO), Biological Oxygen
Demand (BOD5), Chemical Oxygen Demand (COD), Total Suspended
Solids (TSS), Ammoniacal Nitrogen (NH3-N), Colour, Turbidity, Iron,
and Manganese were selected to be measured.
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ii. Land use data such as forestation, agriculture, industrial and residential at
the catchment area were focused. The pollution from non-point sources
may include sediment and toxic contaminants.
1.6 Significance of Study
Today, there are many human activities that cause environmental damage and
deterioration of water quality in developing countries. Human activities such as
industrial, mining and agriculture can cause the degeneration of water quality at
water treatment plants. Therefore, the river should be restored from any
contamination before being treated at the water treatment plant. However, this study
was conducted to find out the main causes that lead to changes in the aesthetic value
of the water supply from PSWT. The current condition of water quality at Sungai
Semantan can be analysed and effective precaution steps should be taken.
GIS was used to generate the visual concentration sources of pollution that
lead to problems with consumer issues. All the data evaluated will use the data
collecting technology of Global Positioning System (GPS) that has been widely used
in GIS. Water quality analysis was conducted at the upstream of the river from
Sungai Bentong and Sungai Kelau. The data compiled to a map using Arc Gis 10.1.
The system allows the delimitation of the pollution patterns across the catchment
area.
This study would provide the responsible authorities with digital information
and permanent database that could provide a quick and cost-effective solution
assessment and mitigation of the future problem related to water quality. It is
important to identify the source of pollution to develop an implementation plan to
eliminate those critical sources. Besides that, this study aimed at employing this
technology in the environment and hope it can help the management in designing
new control structures to improve the water quality standard in Malaysia.
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REFERENCES
Al-Badai, F., Othman, M. S. and Gasim, M. B. (2013). Water Quality Assessment of
the Semenyih River, Selangor Malaysia. Journal of Chemistry.13 (1):331-338.
Babin, N., Mullendore, N. D., and Prokopy, L. S. (2016). Using Social Criteria to
Select Watersheds for Non-Point Source Agricultural Pollution Abatement
Projects. Land Use Policy. 55: 327–333.
Bruce, I. D. and Skipton, S. O. (2014). Drinking Water: Iron and Manganese.
University of Nebraska- Lincoln: United States.
Chan, N. W., Kung, H. T. and Ismail, W. R. (2000). Hill Land Development, Soil
Erosion and Sedimentation as Factors Affecting Water Resources and
Downstream Flooding in Malaysia. United States Regional Conference -
"Southeastern Division Association of American Geographers (SEDAAG) 2000
Conference". 19 -21 November 2000, Chapel Hill, North Carolina, USA.
Davis, H. T., Marjorie, A. C., McDermott, S., and Lawson, A. B. (2009). Identifying
Natural and Anthropogenic Sources of Metals in Urban and Rural Soils using
GIS-Based Data, PCA, and Spatial Interpolation. Environmental Pollution.
157(8–9): 2378–2385.
Davis, M. L. and Masten, S. J. (2004) Principles Environmental Engineering and
Science. (6th ed.) New York :Mc Graw Hill.
DOE (2015). Malaysia Environmental Quality Report 2014, Department of
Environment, Malaysia.
86
Florescu, D., Ionete, R. E., Sandru, C., Iordache, A. and Culea, M. (2011). The
Influence of Pollution Monitoring Parameters in Characterizing the Surface
Water Quality From Romania Southern Area. Romanian Reports of Physics,
56(7–8): 1001–1010.
Grayson, R., Kay, P., Foulger, M., and Gledhill, S. (2012). A GIS based MCE Model
for Identifying Water Colour Generation Potential in UK Upland Drinking
Water Supply Catchments. Journal of Hydrology. 420–421: 37–45.
Hornero, J., Manzano, M., Ortega, L., and Custodio, E. (2016). Integrating Soil
Water and Tracer Balances, Numerical Modelling and GIS Tools to Estimate
Regional Groundwater Recharge: Application to the Alcadozo Aquifer System
(SE Spain). Science of the Total Environment. 568: 415–432.
Jain, C. K., Bhatia, K. K. S. and Seth, S. M. (1998). Assessment of Point and Non-
point Sources of Pollution Using a Chemical Mass Balance Approach.
Hydrological Sciences Journal. 43(3):379–390.
Kadhem, A. J. (2013). Assessment of Water Quality in Tigris River –Iraq by Using
GIS. Natural Resources, 4, 441-448.
Lee A. H and Nikraz H., (2015) BOD:COD Ratio as an Indicator for River Pollution,
International Proceedings of Chemical, Biological and Environmental
Engineering, 88(15).
Mashagbah A., Adamat, R. and Salameh, E. (2012). The use of Kriging Techniques
with in GIS Environment to Investigate Groundwater Quality in the Amman-
Zarqa Basin/Jordan. Research Journal of Environmental and Earth Sciences,
4(2),177-185.
Maimon, A. A. and Zainudin, Z. (2013). Sustainable River Water Quality
Management in Malaysia. IIUM Engineering Journal, 14(1), 29–42.
87
Malakootian, M., Mansoorian, H. J. and Moosazadeh, M. (2010). Performance
Evaluation of Electrocoagulation Process Using Iron-Rod Electrodes for
Removing Hardness from Drinking Water. Desalination, 255(1–3), 67–71.
Nagalakshmi, R., Prasanna, K. and Chandar, P. (2016). Water Quality Analysis
Using GIS Interpolation Method in Serthalaikadu Lagoon, East Coast Of India.
Rasayan Journal Chemistry, 9 (4), 634 - 640.
Ngah, M. S. Y. and Othman, Z. (2011). Impact of Land Development on Water
Quality in Peninsular Malaysia. Malaysian Journal of Environmental
Management. 12(2),113-120.
Naubi, I., Zardari, N. H., Shirazi, S. M., Ibrahim, N. F. and Baloo, L. (2016)
Effectiveness of Water Quality Index for Monitoring Malaysian River Water
Quality, Pollution. Journal. Environment. Studies, 25(1), 231-239.
Oke, A. O. and Ogedengbe, K. (2013). Mapping of River Water Quality Using
Inverse Ogun-Osun River Basin , Nigeria. Lanskap & Environment, 7(2), 48–
62.
Othman, F., Eldin, M. E. A. and Mohd Nor, M. K. (2011). Assesment of a Tropical
Urban River Using GIS-Based Modeling. Advanced Materials Research, 250–
253, 2949–2952.
Othman, F. and Eldin, M. E. A. (2014). Linking The Water Quality Model with GIS
and Ambient Phenomena. International Conference on Innovative Trends in
Multidisciplinary Academic Research, 1, 147–156.
Ozsahin, E. and Atasoy, A. (2014). Soil Erosian Estimation in Lower Asi River
Catchment Using GIS. Procedia, 120, 730–739.
Qasim, S. R., Motley, E. M. and Zhu, G. (2000). Water Works Engineering. (1st ed.)
Texas: Prentice Hall .
88
Saher, F. N., Nasly, M. A., Abdul Kadir T.A, Teruggi, G. and Hossain, M. A. (2012).
Environmental Degradation in Malaysia’s Pahang River Basin and its Relation
with River Pollution : Strategic Plan from Assessment to Mitigation using Geo-
Informatics. International Conference on Energy, Environment and Sustainable
Development, Jamshoro, Pakistan.
Sharma S., Kumar P. Ranjan M. R., Singh U. K., Jindal T. (2017) Water Quality
Monitoring of Yamuna River by Using GIS Based Water Quality Index in
Delhi, India. International Journal of Current Microbiology and Applied
Sciences, 6(2): 1249-1263.
Suratman, S., Sailan, M.I., Hee, Y. Y., Bederus, E. A. and Latif M. T. (2015). A
Preliminary Study of Water Quality Index in Terengganu River Basin,
Malaysia. Sains Malaysiana, 44(1):67-73