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Strategic Water Reserve: New Approach for Old Concept in GCC Countries

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1. General background In the last three decades, rapid population growth and accelerated socioeconomic development in the GCC countries were associated with a substantial increase in water demands, which have escalated from less than 5 billion cubic meter in 1970 to about 26.778 billion cubic meter in 2005. These demands have been driven mainly by agricultural consumptions and by rapid urban expansion. Efficient sustainable and integrated development and management of water resources requires water policy reforms with emphasis on supply and demand management measures and improvement of the legal and institutional provisions. Due to the deterioration of non renewable aquifers, all GCC countries rely on the desalinated water as a main source for domestic water supply. It has been argued that the best long-term solution for the water crises in the domestic sector is to build a network of large-scale desalination plants. The problem facing the GCC countries is the vulnerability of desalination plants to pollution and emergency conditions. The maximum stored water in the ground reservoirs and distribution network is enough only for 24 hours except Sudia Arabia and Kuwait, which is 3 and 5 days respectively as shown in Figure (1). So, in any crises or emergency condition the stored water will not be enough to cover the demand. Also, the production of desalination plants is constant and the demand is not constant. Figure 1; Storage capacity for emergency water in GCC countries.
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Strategic Water Reserve: New Approach for Old Concept in GCC Countries
Dr. Mohamed A. Dawoud
Manager, Water Resources Department, Environment Agency - Abu Dhabi, P.O. Box 45553, Email:
mdawoud@ead.ae
1. General background
In the last three decades, rapid population growth and accelerated socioeconomic
development in the GCC countries were associated with a substantial increase in water
demands, which have escalated from less than 5 billion cubic meter in 1970 to about
26.778 billion cubic meter in 2005. These demands have been driven mainly by
agricultural consumptions and by rapid urban expansion. Efficient sustainable and
integrated development and management of water resources requires water policy
reforms with emphasis on supply and demand management measures and
improvement of the legal and institutional provisions.
Due to the deterioration of non renewable aquifers, all GCC countries rely on the
desalinated water as a main source for domestic water supply. It has been argued that
the best long-term solution for the water crises in the domestic sector is to build a
network of large-scale desalination plants. The problem facing the GCC countries is the
vulnerability of desalination plants to pollution and emergency conditions. The maximum
stored water in the ground reservoirs and distribution network is enough only for 24
hours except Sudia Arabia and Kuwait, which is 3 and 5 days respectively as shown in
Figure (1). So, in any crises or emergency condition the stored water will not be enough
to cover the demand. Also, the production of desalination plants is constant and the
demand is not constant.
Figure 1; Storage capacity for emergency water in GCC countries.
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1
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Kuwait Qatar Bahrain Sudia
Arabia United Arab
Emirates
Reserve (Days)
The possible alternatives for reserving fresh water sources for emergency and peak
demand conditions are 1) to increase ground reservoirs and distribution network storage
capacity or 2) using groundwater aquifer storage and recovery system (ASR). It has
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proved that increasing the capacity of the ground reservoirs and network is very
expensive and not environmental friendly. One of the good solutions is to store this
water in the groundwater aquifers.
Unlike surface ground reservoirs, the water can not be reserved for more than 48 hours,
otherwise it will become stagnant water and not suitable for domestic use. ASR systems
allow for multi-year storage keeping water protected in good quality. Usually, wells can
be located where most needed and because wells require little land, the costs of large
land acquisitions are avoided. Moreover, large water volumes can be stored
underground, decreasing the need for surface reservoirs construction with no
environmental effects when compared with surface reservoirs.
2. What is Aquifer Storage and Recovery?
ASR is a proven way to safely store excess water underground when it is available, and
recover that water for use when supplies are short. For fuller utilization of desalinated
water, and hence further cost reduction, greater water storage capacity is required. To
this end, aquifer storage recovery (ASR) could be used. This is a system that has been
in use in the USA since 1984. It has been developed to improve the use of water supply
and water treatment facilities. The system involves the use of injection wells for the
underground storage of treated drinking water in a suitable aquifer when the capacity of
water supply facilities exceeds the demand, and its subsequent recovery from the same
well to meet seasonal, peak, emergency or long-term demand as shown in Figure (2).
ASR may be used to store surplus water in this way. Also where electricity from a dual-
purpose plant is in low demand ASR can be used to inject desalinated water into the
aquifer as shown in Figure (3). Such seasonal storage may amount to millions of cubic
meters through a single well, compared to a few hundred stored in conventional ground
or elevated storage tanks to meet demand variation. Aquifer storage recover is low cost
where a suitable aquifer is available, since land requirements are minimal.
Figure 2: Aquifer storage and recovery system.
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Figure 3: Typical aquifer storage and recovery operating schedule.
It has been shown that by making more efficient use of existing water supply systems,
ASR can reduce capital costs by 50% to 90%. However, this system has not yet been
used on wide range within GCC countries, although it has been tested in Kuwait, Saudi
Arabia, United Arab Emirates and Oman. In each of these countries it has been planned
in conjunction with desalination facilities to provide a strategic water reserve for
emergency supplies while also meeting other secondary objectives such as seasonal
peak demands, recharging brackish water reserves, and salinity intrusion control. In
June 1993 there were approximately 60 ASR projects in operation or under
development in the USA. Treatment of the recovered water is generally unnecessary
apart from disinfection. There is some evidence that ASR results in the elimination of
the undesirable by-products of chlorination.
3. GCC countries experience in ASR
The concept of strategic water reserve in GCC countries is not new. Artificial recharge
for the groundwater aquifer system was first tried in Kuwait by Parsons in 1964. A
recharge basin in Rawdhatain depression was used to collect the surface run-off during
the occasional rainstorm and then seeped to aquifer system by gravity. Another test in
the same place was carried out during 1972-1973 by injecting desalinated water in two
wells for 27 days. Further efforts wad done in mid 1990’s to investigate the potentiality
of inject the fresh water in Dammam limestone formation in Sulabiya. 4.3 Million Gallon
was injected during a period of 30 days. The results were not conclusive and suggested
limited storage and recovery potential.
IN United Arab Emirates (UAE), the first proposal was submitted to the government by
the United State Geological Survey (USGS) and National Drilling Company (NDC) in
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1998 to. It was proposed to inject 220,000 Gallon a day for 200 days in the Eastern
Region near Al Ain City. The proposal was not accepted due to the cost and limitation of
the availability of fresh water. A pilot test has been carried out in the western region
near Madient Zayed, started in 2002, to inject 2.5 million gallons a day of desalinated
water through five injection wells and infiltration basin. On the other hand, in 2003, after
the construction of pipeline for Qedfaa desalination plant in Fujairah, a detailed
feasibility study was done and a pilot test carried out in Al Shwieb area. Both pilot
projects proven an efficiency of about 85%.
In Qatar, a feasibility study for large scale artificial recharge schemes was to evaluate
the injection of desalination water in Rus and Umm er-Radhuma formation during 1992-
1994. The study concluded the potentiality of building up groundwater reserves in both
aquifer systems.
3. Abu Dhabi Emirate Case Study
3.1 The present storage Capacity for Emergency
Abu Dhabi Emirate many relay on the desalinated seawater/brackish groundwater as
main sources for domestic supply. The total present desalination capacity is about 635
MIGD as shown in Figure (4). Abu Dhabi Water and Electricity Authority (ADWEA),
which is responsible for providing water and electricity for the emirate, uses many
desalination techniques to produce water including Multi Effect Distillers (MED),
Reverse Osmosis (RO) and Multi Stage Flash (MSF). The main technology used is
thermal desalination using MSF because it is a very efficient system that produces high
quality water (2–150 mg/l TDS) in large quantities and has a low risk of bacterial or
pathogenic contamination. At each desalination plant, there are water storage tanks for
back-up use. The size of potable fresh water tanks at the desalination plants varies from
0.2–0.4 Mm3. The total amount of storage at all plants is 1.51 Mm3 which is less than
one day’s production as illustrated in Table (1). The arid climate in the emirate results in
increased consumption in the summer months. Production reflects this increased
summer demand. In the winter months of January and February, production declined
slightly and then gradually increased through the spring months of March and April.
Production for the hottest summer season from May through August shows another
gradual increase. Thereafter, the production attained constancy until the end of
December.
Table 1: Present Storage Capacity (2007).
Company Storage capacity (Mm3)
Umm Al Nar Power Company 0.45
Bainounah Power Company 0.14
Al Mirfa Power Company 0.11
Emirates CMS Power Company 0.23
Gulf Total Tractable Power Company 0.32
Al Taweelah Power Company 0.23
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Figure 4: Daily Abu Dhabi Desalination Capacity.
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630 MGD
101
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During the peak summer season, all the water that is produced is directly consumed,
but in winter there is excess production. This excess is used for the irrigation of
landscaping in public spaces throughout the Abu Dhabi Emirate (Shams El Din et al.
1997). An alternative would be to store this excess water in aquifers during the winter
months and recover it when needed. To maintain an uninterrupted supply during times
of emergency (natural disasters, industrial accidents, war and other crises), the emirate
needs to have long-term storage capacity equivalent to at least 1 year’s fresh water
demand. Two sites were selected and two pilot projects ware carried out starting 2002.
The first one is in Al Shweib in Eastern Region and the other is in the Western Region
as shown in Figure (5).
In the eastern region project water from Qedfaa plant was injected in the shallow alluvial
aquifer system. The results of the study indicate that ASR is a viable alternative for
augmenting the depleted aquifer (Dawoud 2007). The second project was located west
of the highway between Madinat Zayed and Meziyrah. It was designed for an infiltration
capacity of 500 m3/h and recovery capacity of 750 m3/h. A shallow to medium-deep
aquifer north of the Liwa Crescent was selected as the study area for the following
reasons: (1) existence of a large natural fresh groundwater lens (salinity less than 1,500
ppm, partly meeting the TDS-limit of the international World Health Organization
drinking water standard (1,000 ppm), (2) sufficient lateral extension and aquifer
thickness, (3) sufficient depth of groundwater table, (4) relatively homogenous lithology,
(5) far from already existing well fields and (6) favorable hydrochemical conditions. This
study has clearly shown that the recharge of desalinated water into and efficient
recovery from an existing freshwater aquifer are feasible on a large scale (GTZ 2002).
4. Conclusions and Recommendations
All GCC countries relay on the desalinated water as a main source for domestic water
supply. The maximum capacity of emergency reserve in the surface ground reservoirs
and distribution network ranges between 5 to 2 days. This storage can not cover long
period crises and increasing the storage capacity using surface reservoirs is costly and
not environmental friendly. Groundwater storage using the artificial recharge technique
is a promising tool for strategic water reserve in all GCC countries. Storing the fresh
water in groundwater aquifers is more save and more reliable and fixable for use in
terms of time and location. It is recommended to carry out more extensive studies to
evaluate the feasibility of artificial recharge schemes.
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Figure 5: Location of two ASR projects in Abu Dhabi Emirate.
... More than half of Algeria and Morocco aquifers and one-quarter of Tunisia aquifers are overexploited (Fienen and Arshad, 2016). All GCC aquifers are heavily threatened by salinization, which causes quality deterioration and pollution from surface anthropogenic activities (Dawoud, 2008). Future projections show a larger scarcity in groundwater. ...
... MAR has also improved the groundwater quality in Tunisia (Bouri and Dhia, 2010), Morocco (Bennani et al., 1992), and Egypt (Ghodeif et al., 2016;Shamrukh and Abdel-Wahab, 2008) and reduced seawater intrusion in Sebaou Basin (Algeria) (Kadri et al., 2011), and Korba coastal aquifer in Tunisia (Comte and Bachtouli, 2019). Dillon et al., 2018;El-Arabi, 2012;Ghodeif et al., 2016;Shamrukh and Abdel-Wahab, 2008;Van Ginkel et al., 2009) Palestine (Adbul-Hamid, 2008;Ajjur and Mogheir, 2020b;Al-Batsh et al., 2019;Al-Khatib et al., 2019;Alim et al., 2020;Rahman et al., 2013) Jordan (Alraggad and Jasem, 2010;AQUASTAT-FAO, 2018;Ghaida and Elias, 2019;Salameh et al., 2019;Talozi, 2007;Wolf et al., 2007;Xanke et al., 2015;Xanke et al., 2017) Saudi Arabia (Abderrahman, 2005;Al-Othman, 2011;Al-Muttair et al., 1994;AQUASTAT-FAO, 2018;Missimer et al., 2014;Odhiambo, 2016) Syria (AQUASTAT-FAO, 2018;Kattan et al., 2009;Tröger and Wannous, 2016;Wannous et al., 2016;Wannous and Natouf, 2009) Lebanon (AQUASTAT-FAO, 2018;Ibrahim et al., 2019;Khadra and Stuyfzand, 2019;Klingbeil, 2012;Masciopinto, 2013) Iraq (Abdulla et al., 2002;AQUASTAT-FAO, 2018;Stevanović, 2015;Stevanovic and Iurkiewicz, 2008;Wannous and Natouf, 2009) Iran (Abbasi et al., 2019;Ahmadi et al., 2010;AQUASTAT-FAO, 2018;Arzani, 2010;Hashemi et al., 2013;Hashemi et al., 2014;Kalantari and Goli, 2005;Kalantari and Rangzan, 2000;Salajegheh and Keshtkar, 2005;Salih, 2006;Vardanjani and Farjadian, 2012;Yaraghi et al., 2019) Yemen (AQUASTAT-FAO, 2018;Wahib Saif, 2009) Oman (Abdalla and Al-Rawahi, 2013;Al-Shukaili and Kacimov, 2019;AQUASTAT-FAO, 2018;Dillon et al., 2018;Kacimov et al., 2012;Kacimov et al., 2019;Klingbeil, 2012;Luxton et al., 1991) Kuwait (Al-Senafy and Sherif, 2005;Klingbeil, 2012;Mukhopadhyay et al., 2013;Mukhopadhyay and Fadlelmawla, 2009;Mukhopadhyay et al., 1994) Bahrain (Klingbeil, 2012;Naik et al., 2017) (Salameh et al., 2019;Xanke et al., 2017), Egypt (Dillon et al., 2018;Ghodeif et al., 2016), Iraq (Stevanović, 2015), Lebanon (Daher et al., 2011), Syria , United Arab Emirates (UAE; (Dawoud, 2008), and Tunisia (Comte and Bachtouli, 2019). MAR challenges in the MENA region can be categorized into three primary concerns: technical issues, health-risk issues, and socioeconomic aspects. ...
... Heterogeneity in karst aquifer characteristics causes significant clogging and influence dispersion, and, hence, reduces the recovery rate (Daher et al., 2011;Van Ginkel et al., 2009 injecting ~16,000 m 3 of water during 30 days into the Dammam Formation in Sulabiya in the mid-1990s. All these attempts failed due to low rates of recharge and uptake (Dawoud, 2008). ...
Thesis
Full-text available
Sustainable management and augmentation of aquifers are major challenges for arid countries like Qatar. Qatar has a hyper-arid climate characterized by minimal rainfall and extremely high temperatures. Over the last two decades, the country’s population has risen fivefold, Doha urbanization has risen eightfold, and per-capita water consumption has reached an unprecedented rate. The combined effects of these factors pressurized the country’s aquifers, leading to severe water shortages (e.g., water table decline and storage losses) and high deteriorations in quality (e.g., seawater intrusion). This hinders the current expansion of agricultural activities and food security, and, therefore, threatens a critical development pillar of the Qatar National Vision 2030: ensuring “Food Security and Safety”. The challenge, therefore, is to stop the enduring depletion and to manage and augment aquifer storage while at the same time meeting increased demands. This complex challenge exhibits the dire necessity of an integrated approach for the sustainable management of aquifers based on understanding their response to human needs and climatic stresses.The stepwise methodology comprised four parts. The first step included historical data collation, analysis, and future projections of demand. The study proceeded by projecting climatic data through 2100 under two representative concentration pathways using an ensemble of climate models. Following that, a physically-based spatially distributed hydrological model was built to estimate groundwater recharge. Some field and lab work was conducted to analyze evapotranspiration losses and characterize hydraulic properties. Then, the consequent impact on the groundwater system was simulated using 3D finite-difference-based groundwater flow model. The resulting change in groundwater depth and storage were simulated, and consequently, modeling results were used to examine possible scenarios for aquifer protection against climate change and anthropogenic impacts. While Qatar is the case study, the proposed approach is also applicable in arid areas with similar characteristics.
... More than half of Algeria's and Morocco's aquifers and onequarter of Tunisia's aquifers are overexploited (Fienen & Arshad, 2016). All GCC aquifers are heavily threatened by salinization, which causes quality deterioration and pollution from surface anthropogenic activities (Dawoud, 2008(Dawoud, , 2011. Future projections show a larger scarcity in groundwater. ...
... MAR has also improved the groundwater quality in Tunisia (Bouri & Dhia, 2010), Morocco (Bennani et al., 1992) and Egypt (Ghodeif et al., 2016;Shamrukh & Abdel-Wahab, 2008), and reduced seawater intrusion in Sebaou Basin (Algeria) (Kadri et al., 2011) and Korba coastal aquifer in Tunisia (Comte & Bachtouli, 2019). (Dillon et al., 2018;Ghodeif et al., 2016), Iraq (Stevanović, 2015), Israel (Guttman et al., 2017;Idelovitch & Michail, 1985), Lebanon (Daher et al., 2011), Syria and the UAE (Dawoud, 2008), and Tunisia (Comte & Bachtouli, 2019). MAR challenges in the MENA region can be categorized into three primary concerns: technical issues, health-risk issues and socioeconomic aspects. ...
... Examples from Kuwait include Parson's experiment in 1964, another experiment in 1973 where for 27 days desalinated water was injected into two wells, and injecting approximately 16,000 m 3 of water for 30 days into the Dammam Formation in Sulabiya in the mid-1990s. All these attempts failed due to low rates of recharge and uptake (Dawoud, 2008). Another study from Lebanon concluded the non-feasibility of MAR, via infiltration ponds or injection wells, to the main Damour aquifer (Daher et al., 2011). ...
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The study critically reviews the application, management and challenges of managed aquifer recharge (MAR) in the Middle East and North Africa (MENA) region through a survey of 142 studies. The survey reveals the objectives and methods of MAR in the region. It also shows the technical and socioeconomic challenges that significantly cause MAR failure in MENA countries. The article concludes by presenting a framework to evaluate MAR feasibility and it provides recommendations and guidance for future studies and MAR designs in the MENA region, which is facing the impact of climate change.
... First, the increased water demand of a fast-growing population; second, the low (less than 100 mm/year) average precipitation; third, a very high evaporation rate (two to three m³ per year) (ibid); and fourth, the limited recharge of the groundwater [4,17]. For this reason, AD has no choice but to supply domestic water from seawater desalination [17] using techniques such as multi effect distillers (MED), reverse osmosis (RO), and multistage flash (MSF) [18,19]. The main technology used in the UAE is thermal desalination with MSF (57%) because it is more energy efficient and can produce higher quality water (ibid.). ...
... The main technology used in the UAE is thermal desalination with MSF (57%) because it is more energy efficient and can produce higher quality water (ibid.). MED are used at 6% for desalinating water and RO at 37% [19,20]. However, as shown in Table 1, the technique of desalination is still highly energy intensive: RO and MSF technologies use between four-kilowatt hour per cubic meter (kWh/m³) to 7.5 kWh/m³ average and up to 15.40 kWh/m³, respectively [20]. ...
... First, the increased water demand of a fast-growing population; second, the low (less than 100 mm/year) average precipitation; third, a very high evaporation rate (two to three m 3 per year) (ibid); and fourth, the limited recharge of the groundwater [4,17]. For this reason, AD has no choice but to supply domestic water from seawater desalination [17] using techniques such as multi effect distillers (MED), reverse osmosis (RO), and multistage flash (MSF) [18,19]. The main technology used in the UAE is thermal desalination with MSF (57%) because it is more energy efficient and can produce higher quality water (ibid.). ...
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This paper documents a water:energy greenhouse gas (GHG) metric methodology for a decentralized non-potable water system that was developed as part of a Professional Doctorate in Engineering (DEng) research project by the first author. The project identified the need to investigate the challenges in changing the use of potable water to recycled water for landscape irrigation (LI) and for water features (WFs) at a medical facility case study (MFCS) in Abu Dhabi (AD) (the capital city of the United Arab Emirates (UAE). The drivers for the research project were based on the need for AD to decrease desalinated potable water as well as reduce the environmental impact and operational costs associated with the processing and use of desalinated water. Thus, the aim of the research discussed and presented in this paper was to measure the impact of using recycled and onsite non-potable water sources at the MFCS to alleviate the use of desalinated potable water and reduce associated energy consumption, operational costs, and GHG emissions (latterly in terms of carbon dioxide equivalent (CO2e), for LI and WFs. The analysis of three case scenarios at the MFCS compared different approaches to alleviate energy use, costs, and GHG impacts for the use of recycled water in LI and WFs against a baseline. The findings led to a proposed sustainable water conservation and reuse (SWC) strategy, which helped save 50% desalinated potable water for LI use by soil improvement, building water system audits, and alternate non-potable water reuse. The recommendations for this paper are to develop a SWC strategy forming the basis for a water protocol by the competent authority for regional medical facilities including an assessment methodology for building decentralized non-potable water systems to measure their energy, GHG emissions and financial impact.
... ASR has been used in USA since 1984 for water stor- age, including storage potable level TSE. Between 1992 and1994, the possibility of implementing ASR in Qatar by inject- ing desalted water in Rus and Umm er-Radhuma formation had been studied [59]. It was found that ASR can be suc- cessfully implemented to store water in both Rus and Umm er-Radhuma formation. ...
... It was found that ASR can be suc- cessfully implemented to store water in both Rus and Umm er-Radhuma formation. Furthermore, in 2002, two pilot plant tests have been carried out in Abu Dhabi (Madinet Zayed) and (Al Shwieb area) to store 2.5 MIGD of desalinated water and a full feasibility study has been conducted and showed that both pilot plants exhibited recovery efficiency of about 85% [59]. Missimer et al. [60] have investigated the possibility of applying ASR in the GCC and the Middle East and North Africa region. ...
... Missimer et al. [60] have investigated the possibility of applying ASR in the GCC and the Middle East and North Africa region. They found that when mega storage capacities are required, conventional ground-storage are not econom- ically feasible and ASR can offer an economically-feasible storage capacity when desalinated water is stored [59]. The storage of TSE should be implemented in Qatar as it provides cost-effective strategic water storage units which can be used as a source of drinking water. ...
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... This approach would overcome any interruptions in the water supply caused by emergencies and the minimum 1 year time needed required to construct a new desalination plant (Al-Katheeri, 2008). Three ASR pilot projects of artificial recharge have been planned in the UAE, the first operational ASR in Nizwa, Sharjah, one in the western region Liwa and the other one in Eastern District of Abu Dhabi Emirate Al Ain region (Hutchinson, 1998;Al-Katheeri, 2008;Klingbeil, 2012;Dawoud, 2014). ...
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... Seasonal water and electricity demand fluctuations can be met through gas-fired plants adjusting their outputs of each, though there are limitations to plant flexibility which lead to significant inefficiencies. During the winter, electricity needs require running desalination units in excess of water needs, and during the summer both electricity and water demands peak simultaneously leading to efficiency losses in electric generation capacity of gas-fired plants (Dawoud, 2009). ...
Technical Report
https://gw-mena.iwmi.org/wp-content/uploads/sites/3/2017/04/Rep.15-Groundwater-governance-in-Liwa-oasis-report_final_cover.pdf By providing an integrated case study of groundwater, utilization in the Emirate, this report aims to accomplish the following goals: I. Review the baseline physical parameters of local groundwater resources; II. Describe modern agricultural production and forestry systems; III. Discuss institutional and agricultural management challenges and planned reforms; IV. Evaluate the impacts of groundwater utilization on the aquifer system.
... The low levels of water storage are also reflected in the low hydropower generation, which accounts for less than 2% of total electricity generation, apart from Egypt (7-10% from the High Aswan Dam and declining), Morocco (5%), and Iraq (4%) (International Energy Agency, 2016). Given the limits to expansion of surface water storage and increasing variability predicted under climate change, countries are increasingly resorting to aquifers to store water (Dawoud, 2008;Dillon et al., 2019;Lopez et al., 2014). ...
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Abstract Water scarcity in the Arab region is intensifying due to population growth, economic development, and the impacts of climate change. It is manifested in groundwater depletion, freshwater ecosystem degradation, deteriorating water quality, low levels of water storage per capita, and added pressures on transboundary water resources. High‐income Arab countries have sought to circumvent the ever‐present challenges of water scarcity through agricultural imports (virtual water trade), desalination, and, increasingly, wastewater reuse. In this review article, we argue that the narrative of water scarcity and supply‐side technological fixes masks more systemic issues that threaten sustainable water management, including underperforming water utilities, protracted armed conflict and displacement, agricultural policies aimed at self‐sufficiency, evolving food consumption behaviors, the future of energy markets, and educational policy. Water management challenges, particularly on the demand side, and responses in the Arab region cannot be understood in isolation from these broader regional and international political and socioeconomic trends. Recognizing the complex and interdependent challenges of water management is the first step in reforming approaches and shifting to more sustainable development outcomes and stability in the Arab region and beyond.
... Currently the UAE has only a two-day desalinated water storage capacity, making the country vulnerable to any disruption in its desalination plants [3]. Abu Dhabi has embarked on a massive US$5 billion program, based on the aquifer storage and recovery approach, to use local aquifers as strategic reserves for desalinated water [12]. ...
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This paper presents the case for soil and water conservation combined with waste recycling strategies in a desert type climate healthcare environment, which is based on the need for Abu Dhabi to decrease desalinated potable water consumption and increase its waste recycling rate to reduce environmental impact. The work documented in this paper forms part of the first author's Professional Doctorate change project in the United Arab Emirates (UAE), at a medical facility in use since 2015. The project is investigating two aspects: the feasibility of reusing both the site produced organic biological waste as an organic fertilizer and the effluent produced for landscape irrigation. For this paper the sole aspect of the effluent will be discussed. The context is a newly built medical facility in Abu Dhabi with a 21,600m² building footprint area surrounded by a 29,000m² vegetated open spaces. The city, located on the south west coast of the UAE, is dominated by sandy and salty soil, high temperature and humidity [1]. Five types of effluent generated by three types of dehydrators have been tested for general characteristics, inorganic and organic compounds, and metal parameters and analysed against local authorities’ parameters limits to verify compliance and establish suitability for landscape irrigation and water feature reuse. The effluent test results show absence of microbiological contaminants. The quality of the effluent shows that secondary and tertiary water treatment would be needed to regulate the BOD, turbidity and pH levels to align with the local regulation water recycling requirements. The next steps are for the facility dehydrator effluent to be tested onsite to provide an account of its quality for reuse and for selecting a tertiary treatment type if necessary suitable for landscape irrigation. This to understand how food waste processed onsite can impact the environment, operation and maintenance cost and practices, greenhouse gas emissions, and building systems energy consumption. This study may be relevant to local competent authorities responsible for making and adjusting standards on non-clinical wastewater reuse and recycling should dehydrators be reused at a larger city scale.
... Almulla et al. (2005) reported that the demand for potable water in Sharjah, UAE ranges from 220,000 to 250,000 m³/day and the total system storage is only 80,000 m³ or between 7.6 and 8.5 hours of total daily demand. Dawoud (2012) suggested that the "storage capacity for emergency" in GCC countries ranged from 2 to 5 days with Kuwait (5 days) being the highest and Qatar, Bahrain and the United Arab Emirates (2 days) being the lowest of those reported. Saudi Arabia was reported to have 3 days of emergency capacity. ...
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Population growth, lack of ground-storage in major metropolitan centers, and a variety of security issues cause the need to develop large storage capacities to meet potable water supply needs during emergency conditions in the GCC/MENA region. Because of the arid nature of the region and the very large storage capacities required, conventional ground-storage and surface reservoirs are not economically feasible to meet strategic storage requirements, but must be used to manage distribution system daily demand fluctuation and short-term emergency needs (fire flow). Aquifer storage and recovery (ASR) is an economic and viable technical solution to meet the critical need for strategic long-term storage. ASR systems that can potentially store billions of cubic meters of desalinated water can be economically developed. These systems need to be sited at strategic locations, such as near water treatment facilities, adjacent to major pipelines conveying post-treated desalinated water to municipal population centers or near to pumping stations associated with municipal high water use centers. Great consideration must also be given not only to the strategic positioning of the ASR reservoirs, but also to the hydrogeology of the aquifers in which the systems would be developed. Not all locations and aquifer systems can successfully support a mega-scale ASR system.
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This paper documents a non-potable water (NPW) quality assessment methodology for a decentralized non-potable water system in Abu Dhabi (AD), capital city of the United Arab Emirates (UAE), which is dominated by sandy and salty soil, high temperature, and humidity. The context is a medical facility case study (MFCS) in AD, which includes a landscape 50% as large as its building footprint. The project identified the need to investigate the impact of air handling unit (AHU) air conditioning (A/C) condensate water (CW) quality on soil health and building hydraulic systems. The aim of the research was to measure the impact of using recycled on-site NPW sources in a MFCS in AD, to alleviate the use of desalinated potable water and reduce associated energy consumption, operation cost, and greenhouse gas emissions for landscape irrigation (LI) and water feature (WF) use. CW has been tested in 2016 and in 2017 and analysed against local authority’s parameter limits to establish suitability for LI and WF use. The findings are that in AD CW classification and characterization is a gap in knowledge whereby salinity and toxicity concentration limits should be addressed by the local authority because CW has an impact on soil infiltration rate due its low dissolved salt content as evidenced by the water test results. The recommendations for this paper are to develop a sustainable water conservation and reuse (SWC) strategy forming the basis for a water protocol by the competent authority for regional medical facility including a methodology for assessing on-site NPW quality for outdoor reuse to reduce soil infiltration problems and consequently conserve water and associated energy. The next steps are to confirm if the MFCS soil infiltration rate is affected by the CW or other factors, and to test additional NPW types.
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