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click hereGROUNDWATER CHARACTERIZATION FOR SUSTAINABLE USAGES IN SOUTHWEST AND NORTHWEST BANGLADESH ON GIS AND WATER QUALITY INDEX (PhD Thesis- Running)
1. INTRODUCTION
Groundwater is the most important source of domestic,
industrial and agricultural water supply in the world. It is estimated that
approximately one third of the world’s population use groundwater for drinking
purpose (Nickson et al. 2005). It is
found in aquifers that have the capacity of both storing and transmitting
water, in significant quantities (Todd 1980). Generally, groundwater quality
depends on the quality of recharged water, atmospheric precipitation, inland surface
water and subsurface geochemical processes (Twarakavi and Kaluarachchi 2006; Kumar
et al. 2014). In coastal regions groundwater quality patterns are complex,
because of the input from different water sources including precipitation,
seawater, ascending deep groundwater and anthropogenic sources (Steinich et al.
1998). Problems in coastal areas are typically connected to contamination of
fresh water resources by saline water and include well field salinization, crop
damage, and surface water quality deterioration (Karro et al. 2004).
Bangladesh lies in the northeastern part of South Asia, has
710 km coastal line and the coastal area covers about 32% of the country (Policy, C. Z. 2005). Although, coastal aquifers serve as major sources of
freshwater supply, the groundwater in coastal region is relatively vulnerable
to contamination by seawater intrusion, which makes groundwater unsuitable (Kim
et al. 2006; Jorgensen et al. 2008). Natural processes and anthropogenic
activities like; over extraction, urbanization and agricultural activities are
the main reason for seawater intrusion and water quality deterioration in
coastal aquifers (Mondal et al. 2011; Selvam et al. 2013). Nowadays, almost 53%
of the coastal areas of Bangladesh are affected by salinity (Hoque et al. 2003;
Woobaidullah et al. 2006). Salinity becomes a major problem in south-western
coastal region of Bangladesh, where irrigation water quality is affected by
high levels of salinity (Shammi et al. 2016), which is a source of irrigation
salinity and it mainly results from rises in the groundwater table due to
excessive irrigation and the lack of adequate drainage for leaching and removal
of salts (Corwin et al. 2007). The total area under irrigation in Bangladesh is
5,049,785 ha and 78.9% of this area is covered by groundwater sources including
3,197,184 ha with 1,304,973 shallow tubewells and 785,680 ha with 31,302 deep
tubewells (DPHE and JICA 2010). However, most crop lands in the coastal areas
of Bangladesh remain fallow in the dry season because surface water resources
are saline and unsuitable for irrigation, while groundwater is not intensively
utilized because of the fear of seawater intrusion into aquifers (Mondal et al.
2008). Seawater intrusion is a major threat in the coastal aquifers of
Bangladesh, especially in southwestern region (Bahar and Reza 2010; Islam et
al. 2015, 2016; Islam and Bhuiyan 2016). The over dependence on groundwater for
drinking, agricultural and industrial sector and different climatic and natural
phenomenon causes coastal groundwater contamination (Srinivas et al. 2015).
Geochemical studies of groundwater provide a better
understanding of water quality and possible changes (Kumar et al. 2014).
However, the coastal groundwater system is fragile and its evaluation will help
in the proper planning and sustainable management (Sefie et al. 2015).
Therefore detailed investigations regarding the groundwater hydrogeochemistry
and water quality in shallow aquifer is imperative. So the present study aims
to investigate the groundwater, to determine its utility and find out the major
geochemical process in study area. It also intended to delineate the spatial
distribution of hydrogeochemical constituents for proper understanding and
future management perspective.
Urban agglomerates in the Lower Bengal Delta, Bangladesh
are characterized by high population density (Ahmad, 2005; Ahmed, 2011), a
poorly maintained and dilapidated built environment (Ahmad, 2005), an
ineffective natural drainage system (SDP, 2011), drainage congestion, and
limited and restricted aquifer recharge (Brammer, 2010; Adri and Islam, 2012; Brammer,
2014; Rakib et al., 2019). Obviously, the scarce resource in such deltaic urban
centres is fresh water, and its availability is delimited because of high population
density, where overexploitation is imminent (Erban et al., 2014; Schmidt, 2015).
The surface water repositories in these regions are also locations of
contaminated and induced salinization (Nobi and Gupta, 1997; Rahman and
Bhattacharya, 2006). The situation exacerbates due to accelerated urbanization
(Burgess et al., 2010; Abedin et al., 2013; Barbosa et al., 2016; Hoque et al.,
2016; Islam et al., 2017) as well. Moreover, the Bengal delta is
environmentally more stressed as compared to other mega-deltas such as that of
the Mekong and Amazon (Brammer, 2014; Szabo et al., 2016).
Khulna (southwest coastal) region of Bangladesh is
designated as one of the most stressed locations globally under the realm of
rapid changes in the climatic pattern (Mondal et al., 2013; Auerbach et al.,
2015; Chatterjee, 2015; Shahid et al., 2016). The Khulna City Corporation (KCC)
is located at the core of the Lower Bengal delta and its urbanization has taken
place at the cost of natural wetlands, including ponds and lakes (Khan et al.,
2016). The KCC accommodates a staggering 1.5 million people within an area of
about 46 km2 (ADB, 2010; Mondal et al., 2013) and the city is the third most
populated urban agglomerate of Bangladesh (Mondal et al., 2013; Khan et al.,
2016). It is under intense stress for potable water because of both in-situ and
ex-situ stressors such as urbanization, climate change, and regional and
upstream interventions on the hydrological regime (Khan et al., 2016). Demands
for potable water in KCC are maintained mainly through groundwater extraction
but is not suitable for most domestic purposes (Adhikary et al., 2012; Datta
and Ghosh, 2015). The surface water bodies such as ponds and lakes are
shrinking and these water-repositories are becoming hubs of urban waste. Khulna
Water Supply and Sewerage Authority (KWASA) is supplying piped groundwater to
only 23% of the urban population (ADB, 2011a; ADB, 2011b). Under such
situations, it is essential to search for additional sources of quality potable
water for KCC residents.
Knowledge on geochemical attributes of water from surface
and sub-surface sources and their mutual geochemical interactions is essential
in assessing suitable geochemical options for water security in coastal
regions.
Quality aspects of groundwater in Khulna City Corporation
(KCC) have been studied by Bahar and Reza (2010) and Adhikary et al. (2012)
among others. Nevertheless, exploring options for potable water through
geochemical exploration of multiple water sources in one of the most
environmentally stressed city like Khulna and
others in this region is lacking.
It is estimated that approximately
one-third of the world’s population use groundwater for drinking (Nickson et
al. 2005). Fresh groundwater is an important resource because of its potable,
agricultural and industrial use. The ever increasing population density in
coastal zones (Finkl, 1994; Vandenbohede et al., 2009) and the demand for
potable freshwater globally (UNEP, 1999; Nickson et al., 2005) renders coastal
groundwater supplies to ceaseless depletion worldwide (Barlow, 2003). Generally
the coastal aquifers are shallower and fragile and are susceptible to
contamination and pollution (Chidambaram et al., 2009). The major threat to
coastal aquifers is saltwater intrusion, sometimes induced because of over
exploitation, due to their proximity to the sea (Nadler et al., 1981; Morell et
al., 1996; Sukhija et al., 1996) and also there are many aquifers deposited in
palaeo-saline environment, mostly in deltas. The variability in hydrochemistry
of coastal aquifers is thus complex due to presence of conflicting processes in
the geoenvironment (Morell et al., 1996).
Urban conglomerates in southwestern
coastal Bangladesh are characterized by high population density (Ahmad, 2005,
2011), poorly maintained and dilapidated built environment (Ahmad, 2005),
restricted and ineffective natural drainage system (SDP, 2011), water logging
but limited recharge due to concrete envelope (Adri and Islam, 2012; Brammer,
2010). The aquifers in such locations are also susceptible to contamination and
induced saltwater intrusion (Nobi and Gupta, 1997; Rahman and Bhattacharya,
2006). A number of generalized studies on groundwater of the southwestern
coastal Bangladesh as a whole and also on specific issues may be found
elsewhere (Nobi and Gupta, 1997; Yokota et al., 2002; Rahman and Bhatacharya,
2006; Bahar and Reza, 2010; Burgess et al., 2010; Haque et al., 2010; Islam et
al., 2011; Rahman et al., 2011; Adhikary et al., 2012; Ghosh et al., 2012;
Khanom and Salehin, 2012; Rahman et al., 2012; Harun and Kabir, 2013). However
understanding hydrochemistry is essential in coastal aquifer management ( Datta
and Ghosh, 2015). The present work would investigate the hydro-chemical nature
of solute load of aquifers in urban conglomerates situated in the southwestern
coastal Bangladesh.
2.
BACKGROUND OF THE STUDY
Ground water is one of the earth’s most
important resources for human life. The water quality depends upon the
geological environment, natural movement, recovery and utilization. Geochemical
processes have an influence on the prevalence of anthropogenic and natural
contaminants in coastal environments (Toda et al 2002). It is estimated that
approximately one third of the world’s population use groundwater for drinking
purposes (Nickson et al 2005). Similarly in Southwest Bangladesh the total
water supplied to a growing mass of about 30 million is groundwater and to some
extent surface water. Urbanization, industrialization, unplanned land use, lack
of people awareness etc. worsen the quality of groundwater (eg. Laluraj et al
2005). Moreover this region comprises Khulna, Satkhira and Bagerhat is always
vulnerable to sea-water intrusion due to coastal proximity. On the other hand,
according to DPHE except the hilly districts arsenic has been identified in the
ground water of 61 districts. This area falls within the western part of
Faridpur Trough of Bengal Foredeep (Alam 1990) which is filled with Tertiary
and Quaternary sand and clay rich sediments with few coarse sand beds (Roy et
al. 2005). Hydrochemistry of groundwater is important to assess the ground
water quality for understanding the suitability for various purposes like
domestic, irrigation, industrial etc. No extended studies in ground water had
so far been carried out in this area, some localized analyses were done but
literature on hydrochemical characterization of ground water is scarce.
3. LITERATURE
REVIEW
The review of literature is one of the
important parts to carry out the research on the field of hydrochemical
characterization of ground water. Number of researches has so far been done in
this country and abroad. According to the research title the present work
mainly focuses on the hydrogeochemical characteristics of ground water in
southwest Bangladesh. Quality based research work is available but more
research should be carried out to get a clear picture. Some important published
papers relevant are discussed here in brief.
Literature on generalized hydrochemical studies
on surface- and groundwater of the south-western coastal (the Lower Bengal
Delta) and other part of Bangladesh may be found elsewhere (Nobi and Gupta,
1997; Yokota et al., 2002; Rahman and Bhattacharya, 2006; Anwar et al., 2008; Burgess et al., 2010; Haque et al., 2010; Islam
et al., 2011; Rahman et al., 2011; Ghosh et al., 2012; Khanom and Salehin,
2012; Harun and Kabir, 2013; Rahman et al., 2014a; Datta and Ghosh, 2015; Akter
et al., 2016; Islam et al. 2016a, b; Ayers et al., 2017; Mostafa et al., 2017; Tanvir
et al., 2017; Datta et al., 2018, Islam et al., 2018; Roy et al., 2018; Md.
Bodrud-Doza et al. 2019; Saha et al., 2019;
Datta et al.,2020; Molla Rahman et al. 2021,
Shaibur, M. R. 2022, Rahman M. M. 2023, Moumita et al., 2023 and elsewhere).
Besides,
different geochemical processes in groundwater governing the chemical
characteristics of groundwater, is well documented in many parts of the world
by many authors i.e., Iren et
al. (1997), Beatriz Helena et al. (2000), Panagopoulos et al., (2004), Laluraj
et al. (2005), Montety et al. (2008), Jalali
(2008), Adepelumi et al. (2009), Manjusree et al.
(2009), Srinivasamoorthy et al. 2011, 2013) Thilagavathi et al. (2012),
Sivasubramanian et al. (2013), Nagaraju et al. (2014), Kumar et al. (2015), ,
Balaji et al. (2016), Halder
et al. (2023) etc.
4.
OBJECTIVES OF THE RESEARCH
4.1
General Objectives
The present research is proposed to
find out temporal and spatial characteristics of hydrochemical parameters of
the ground water in urban cities Southwest Bangladesh, which is essential to
find out security of groundwater as a resource in the study area.
4.2
Specific Objectives
1. To develop physicochemical database
of groundwater in the study area.
2. To investigate physicochemical
database of ground water in the study area.
3. Provide support and services to
water security issues of the region.
| Details | |||
| Role | Co-Supervisor | ||
|---|---|---|---|
| Class / Degree | PhD | ||
| Students | Molla Mohammad Shafiqur Rahman Student ID: PhD 241001 Session- January 2024
Date of Admission: 17/12/2023 | ||
| Start Date | January 2024 | ||
| End Date | December 2028 | ||