Impact of evaporation on groundwater salinity in the arid coastal aquifer, Western Saudi Arabia
Graphical abstract
Introduction
In the arid and semi-arid environments, groundwater management is a challenging task due to lack of water resources, low and erratic rainfall, high evaporation rate, low recharge and climate change (DeNicola et al., 2015, Shrestha et al., 2016, Hu et al., 2019). Water quality degradation often leads to stress in water management and distribution system. Groundwater and soil salinization are largely intensified by evaporation in arid and semi-arid regions (Wu et al., 2014, Re and Sacchi, 2017). In the coastal aquifer, salinization is a global issue that endangers groundwater utilization and management in the arid and semi-arid environments (Vallejos et al., 2020). Evaluating the salinization processes in the coastal aquifer is crucial due to multiple contamination sources and complex processes (Re and Zuppi, 2011, Kloppmann et al., 2013, Nogueira et al., 2019, Ziadi et al., 2019, Vallejos et al., 2020). Further, coastal aquifers often have a shallow water table and are highly vulnerable to surface contamination sources (Vrba and Romijn, 1986, Rosenthal et al., 1992, Zhang et al., 2014, Jaunat et al., 2019).
Numerous articles discussed the groundwater quality and chemistry in the coastal aquifers and arid/semi-arid areas (Rajmohan et al., 2009, Ahmed et al., 2017, Re and Sacchi, 2017, Gamboa et al., 2019, Naeem et al., 2019, Nogueira et al., 2019, Ziadi et al., 2019, Vallejos et al., 2020). Huang et al. (2013) reported that groundwater chemistry in Dongguan, south China, is governed by the seawater intrusion, lateral flow of river water, water-rock interaction, sewage, industrialization and agricultural pollution. Kloppmann et al. (2013) studied the groundwater salinity in French aquifer and stated that seawater intrusion is a predominant process in the coastal aquifer while inland salinity is caused by the evaporites. Comte et al. (2016) studied the groundwater resources management in the coastal aquifer of East Africa and reported that poor hydrological knowledge, lack of longterm monitoring plan and inefficient interaction between stakeholders and local communities are major challenges in these regions. In addition, they stated that shallow wells are less saline compared to deeper one due to saltwater invasion. Ahmed et al. (2017) studied the groundwater chemistry in the coastal volcano-sedimentary aquifer, Djibouti, Horn of Africa and reported that saline water intrusion and geogenic processes affected the groundwater quality. Gamboa et al. (2019) evaluated the origin of groundwater solutes in a hyper-arid environment in Atacama Desert in Chile and reported that atmospheric dust, evaporation and water-rock interaction in various geological formations are contributed well in groundwater chemistry. Earlier studies justified that groundwater chemistry is determined by natural processes and anthropogenic factors (Rajmohan et al., 2017, Li et al., 2019, Rajmohan, 2020). Natural processes such as mineral weathering, evaporation, ion exchange, saline water invasion and associated geochemical processes are prevalent in the coastal aquifer (Rajmohan et al., 2009, Ahmed et al., 2013, Huang et al., 2013, Abdalla, 2015, Gamboa et al., 2019, Nogueira et al., 2019, Ziadi et al., 2019). Likewise, anthropogenic factors namely agricultural, industrial, domestic activities and urban development altered the chemistry of coastal groundwater (Huang et al., 2013, Bamousa and El Maghraby, 2016, Ziadi et al., 2019).
In Saudi Arabia (KSA), rapid developments in agriculture and industrial sectors resulted in tremendous pressure on shallow aquifer. Agriculture (81–83.5%) followed by the industries are the major consumer of groundwater in this country (MoWE, 2014, Chowdhury and Al-Zahrani, 2015). Rainfall and floods are the major recharge sources of shallow aquifers (Zahrani et al., 2011, Masoud et al., 2018). On the other hand, high pumping rates degraded the groundwater resources, both quantity and quality (FAO, 2009, Ziadi et al., 2019). Groundwater quality degradation by various sources is documented well in KSA. The impact of the landfill and dumping sites (Hejazi, 1989, Al-Arifi et al., 2013, Rehman and Cheema, 2016), cesspools and sewage systems (Al-Shaibani, 2007, Alyamani, 2007, Alabdula’aly et al., 2010, Rehman and Cheema, 2017) and municipal and industrial waste (Al-Oud, 2008) on groundwater quality are reported in the literature and these studies mostly documented only the contamination status. Moreover, intensive agricultural activities led to groundwater salinization and nitrate accumulation in the shallow aquifers worldwide (Stigter et al., 1998, Oren et al., 2004, Re and Sacchi, 2017, Gutiérrez et al., 2018, Ziadi et al., 2019). In KSA, the relation between groundwater contamination and agricultural activities is not well documented yet except in few studies (Subyani, 2005, Bamousa and El Maghraby, 2016). Further, source of groundwater salinity and related processes are not explored well in this country. Hence, a detailed knowledge and understanding about the groundwater chemistry and geochemical processes will aid for sustainable management of groundwater resources in this country.
The present study was performed to evaluate the impact of evaporation on groundwater salinity in the arid coastal aquifer of Al Lusub basin, Western Saudi Arabia. Rajmohan et al (2019) reported that groundwater usage is restricted in this basin due to high salinity and contamination. Therefore, a clear understanding of groundwater chemistry is a key factor to manage available groundwater resources in the shallow coastal aquifer. The objectives of this study are to identify the origin of solutes in the groundwater, to evaluate the geochemical processes governing water chemistry and to differentiate the role of evaporation and other factors from seawater intrusion on groundwater chemistry using geochemical and multivariate statistical approaches. In the Al Lusub basin, few studies have been performed to evaluate aquifer sustainability, the impact of pumping rate, groundwater potential and groundwater quality (El-Didy, 1999, El-Hames and Al-Ahmed, 2005, El-Didy, 2006, Ewea, 2011, Rajmohan et al., 2019). The groundwater chemistry in this basin is governed by distinguished sources and processes, which are not well defined in the earlier studies. This study can help to protect and manage this shallow coastal aquifer in an efficient way. Further, the outcomes of this study will contribute to improve the overall knowledge of geochemical characteristics of this shallow aquifer in the arid environment and also will serve as a valuable base for groundwater salinization and pollution assessment in similar arid and semi-arid regions in the world.
Section snippets
Study area
The study area, Wadi Al Lusub, is located in the western part of Saudi Arabia (Latitude: 39° 0′–40° 20′; Longitude: 39° 0′–40° 20′) (Fig. 1) and covers about 2497 km2. The study watershed endures arid climate and the average maximum temperature ranges from 38° to 43° (40°, mean) and the mean minimum temperature varies from 16° to 33° (20° mean). The average relative humidity is between 38% and 62%. The rainfall is highly variable, irregular and short duration with high intensity, which causes
Materials and methods
Groundwater samples (n = 52) were collected from 52 operating wells in the study region during the summer (Fig. 1). Only limited number of wells are available for sampling in the study site, which are not uniformly distributed over the area. Field parameters namely pH, electrical conductivity (EC) and temperature were measured in situ using portable meters (SevenGo Duo SG23, Mettler Toledo). Figure SF2 explains the methodology adopted in this study. Groundwater level was measured using a water
Results and discussion
Groundwater quality in this shallow aquifer is generally neutral to alkaline in nature (pH 6.6–7.8, 7.2 (average); n = 52). The EC ranges from 1291 µS/cm to 25,700 µS/cm with an average of 9780 µS/cm (n = 52) and total dissolved solids (TDS) varies from 646 mg/l to 12860 mg/l with a mean value of 4892 mg/l (n = 52) in the groundwater. Groundwater salinity increased from upstream to downstream (groundwater flow direction) in the study site (Fig. 2, SF1). TDS is greater than 1000 mg/l in 92%
Conclusions
Groundwater in Al Lusub basin is brackish (TDS > 1000 mg/l, 92%) and groundwater in the shallow wells have high concentrations of chemical constituents compared to deeper ones except for HCO3−, silica and pH. HCA classified the water samples into three groups (CG1, CG2 and CG3). Groundwater in the CG1 wells is relatively less mineralized and groundwater salinity increases from CG1 to CG3 wells. Wells in CG3 have a shallow water table, lower pH (<7), HCO3− and silica compared to other groups.
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgement
This project was funded by the Deanship of Scientific Research (DSR) at King Abdulaziz University, Jeddah, under grant no. G-586/123/38. The authors, therefore, gratefully acknowledge with thanks DSR for technical and financial support.
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