Next Article in Journal
The Inequities of National Adaptation to Climate Change
Previous Article in Journal
Magnetic Separation and Enrichment of Fe–Ti Oxides from Iron Titaniferous Beach Sands: Process Design Applied to Coastal Ecuador
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Water Resources Depletion and Its Consequences on Agricultural Activities in Najran Valley

1
Civil Engineering Department, College of Engineering, Najran University, Najran 55461, Saudi Arabia
2
Department of Urban and Regional Planning, College of Architecture and Planning, Imam Abdulrahman Bin Faisal University, Dammam 31441, Saudi Arabia
3
Department of Landscape Architecture, College of Architecture and Planning, Imam Abdulrahman Bin Faisal University, Dammam 31441, Saudi Arabia
4
Department of Building Engineering, College of Architecture & Planning, Imam Abdulrahman Bin Faisal University, Dammam 31441, Saudi Arabia
5
Department of Architecture, Faculty of Engineering, Al-Baha University, Al-Baha P.O. Box 1988, Saudi Arabia
*
Author to whom correspondence should be addressed.
Resources 2022, 11(12), 122; https://doi.org/10.3390/resources11120122
Submission received: 18 October 2022 / Revised: 24 November 2022 / Accepted: 9 December 2022 / Published: 15 December 2022

Abstract

:
This study focuses on highlighting the major effects on the agricultural activities caused by the reduction in water resources in Najran, Saudi Arabia. Since the last decade, there has been a sharp decrease in the availability of water in the area as reported by many researchers due to urban sprawl, excessive groundwater extraction causing a decrease in land fertility, and destruction of soil structure. The water resources of the area and the agricultural heritage is endangered, and also the environmental, economic, and social impact of these actions can be severe if such activities continue in the future. The purpose of the study is to obtain detailed information regarding the major causes of water depletion in the Najran Valley as per the opinion of the residents. A survey questionnaire was designed with a high level of flexibility, covering the key issues including causes of groundwater depletion, factors that affected agricultural activities and irrigation practices and the environmental impact of the Najran Dam, and the risks of floods related to it. An overwhelming response was received from the people of the area. Significant results were obtained from the analysis, and the major effects and causes were highlighted as conclusions. The study shall help the city planners and policymakers in identifying the major causes of water depletion and the actual needs of the residents in order to manage the water resources of the area efficiently. Understanding the public opinion on the issues discussed in this study shall provide a base to develop management options for water resources problems suited to local contexts that fits the need of the community.

1. Introduction

Saudi Arabia, being in the arid region, faces serious water issues and needs the latest techniques and methods to cope with the water demand in terms of the availability of water during its hot and dry climate. The shortage of water adversely hits all the agricultural, industrial, and domestic activities simultaneously. In the past few decades, there has been an increase in the awareness of water shortage, courtesy of the sharp incremental trend of research in this field [1,2]. This all started with the initiative of the Kingdom in establishing an exclusive authority, the Ministry of Agriculture and Water, in 1953, whose sole purpose was to study and research the water resources and agriculture of the Kingdom and work on its improvement. After various evaluations, today, the ministry is known as the Ministry of Environment, Water, and Agriculture [3]. The ministry is performing well for the preservation of water and the environment and improvement in agriculture, including presenting the latest methods and techniques, collecting and analyzing data, preparing administrative frameworks, etc. [3].
There are three major sources of water in Saudi Arabia, namely groundwater, seawater, and rainwater. Groundwater as the major source is found in good quantity in Saudi Arabia near the coastal regions, but it has been in use for a very long time now, and it is feared that the groundwater reserve might be nearing depletion, as it has been reported in various regions that the water table depth has gone down as compared to the previous year’s observations [4]. Regarding the use of seawater, Saudi Arabia is one of the very few countries that started seawater desalination on an industrial scale to fulfill the domestic water demand of its population. It was reported by the General Authority of Statistics that the production of desalinated water in the Kingdom reached 2137 million cubic meters (MCM), with an all-time increasing trend [5]; however, it cannot be relied upon for long, as it is consuming a huge amount of energy resources of the Kingdom [6].
The third source of water for the Kingdom is rainwater. As the country lies in a hot arid climate, the amount of rainfall it receives is very scarce during the year [3]. However, there are many feasible locations around the country where rainwater can be stored by creating reservoirs with the help of dams. Later, the stored water is used mainly for irrigation and domestic purposes. The total number of dams built in Saudi Arabia in various regions up through 2019 was 508 as shown in Table 1, along with their storage capacity [3]. The number of dams constructed in a region is purely based on the amount of rainfall received, requirement of water storage, and the population of that particular region.
Najran is one of the provinces of Saudi Arabia that has a great number of dams, constructed mainly for irrigation and flood control purposes. Najran Province has a total of 27 dams with a storage capacity of 103.86 MCM, contributing 4.6% of the total water storage capacity provided by dams in Saudi Arabia, as shown in Figure 1. Najran is characterized by having an arid climate, where the amount of rainfall varies from year to year and from month to month. Table 2 shows the long-term mean monthly climatic variables in the study area. The highest average monthly temperature is recorded in July and August, whereas relative humidity shows an increasing pattern during winter in December–January and a decreasing pattern during summer from June to August. Rainfall in the study area is observed during two seasons: the first is during the spring season of March–May, followed by the summer season from June to August.
Table 2 also presents the average monthly values of potential evapotranspiration (PET) in mm/day as calculated by JICA [7]. The falling trend of potential evapotranspiration during the winter months is observed due to decrease in average temperature and daylight time.
Table 3 below shows the fluctuation of annual runoff amounts in Najran Valley between 1967 and 1976 in million cubic meters (MCM). These data were recorded before the construction of the Najran Dam and show a marked variation in the annual runoff. In some years, the annual runoff reached three times the annual average, which caused frequent floods in the Najran Valley during this time. Hence, it seemed necessary to construct a dam to reduce the risk of flooding and protect people and their property.
Najran Dam was built in 1980 to protect residents of the valley from frequent floods and reduce the recurring risks in the region. Table 4 below shows the salient features of the Najran Dam. Figure 2 shows a general view of the upstream and downstream of the dam. Since the construction of the Najran Dam, there have been many positive impacts, as the dam has helped to a large extent in reducing the risk of flooding in the region [8]. The dam also contributes to the recharge of groundwater, especially in the areas upstream of Najran Valley.
Since the 2010s, various issues regarding the groundwater table in the Najran Region are being reported. Al-Ghobari [8] reported that the groundwater in the Al Wajid aquifer of Najran is depleting quickly due to the high rate of extraction of water as compared to the rate of recharge. About 79% of the irrigated area in Najran depends entirely on nonrenewable water extracted from deep artesian wells, as documented by Ghanim [10]. The Al Wajid aquifer is a big reservoir of groundwater that is shared by Saudi Arabia and Yemen. Youssef et al. [11] performed a study related to land-use change, and extensive hydrological investigations were conducted over the past years. They concluded that the groundwater table level has decreased significantly over time.
This decrease in the level has caused the formation of earth fissures as long as 600 m with a width and depth of 30–200 cm and 50–400 cm, respectively [6]. These earth fissures are generally observed to have occurred in agricultural land, affecting the productivity of the area. UN-Habitat prepared a comprehensive report on Najran Province, highlighting various issues the area is experiencing recently related to water [6]. These issues are listed below:
  • Appearance of earth fissures caused by excessive water extraction;
  • Lack of water management for self-sustainability;
  • Depleted water table resulting in water shortage and loss of agriculture;
  • Reduction of agricultural land resulting in ecological imbalance.
The excessive groundwater extraction due to the increase in water demand has caused huge damage to the agricultural activities and the water resources of the region. The latest study shows that the depth of the groundwater table is now found to be 120–130 m below the ground level [12]. In a GIS-based study performed by Abd El Aal et al. [13], for the past 45 years, it was concluded that the agricultural land has contracted over the years, and the Najran Valley has become smaller than before.
An extensive literature review was performed to find published studies of public perception related to water resources. Such studies are quite common all around the world, and this strategy was adopted to obtain a direct opinion related to the issues being experienced by the people living in the study area. A study recently performed in Nevada, United States, assessed the possibility of the reuse of potable water and its management [14]. The results showed that the residents of the area showed concern about the depleting water resources and the future of water use. Various suggestions were put forward by the authors to overcome the foreseen crisis of water. Another similar study on water reuse was conducted by Po et al. [15] in Australia. Hua [16] undertook a public perception study on water resource development for the reason of increased water pollution in the suburbs of Malacca River in Malaysia. In another similar study, Zhu et al. [17] reported the results of public perception of the acceptability of reclaimed water in Shandong, China. They concluded that due to water scarcity, the people of the province are willing to accept reclaimed water for domestic use. An earlier study of public perception related to water quality and water conservation in Canada was published by McDaniels et al. [18]. They did research on Lower Fraser Basin in the province of British Columbia and concluded the willingness of the residents for participating in water conservation activities. Regarding Najran, Gasmi and Belloumi [19] conducted a public perception survey to assess the progress of the plan to achieve the sustainability goals. They found a positive effect of the implementation of the plan. Elkhrachy [20,21] highlighted another risk expected for Najran Valley related to flash floods. The authors performed a GIS study to predict the amount and effects of a flash flood in the area. Similar conclusions were put forward by Abd El Aal et al. [22]. Alqahtani et al. [23] performed a study on water quality for the groundwater of the Najran area and stressed that there is a need for a proper monitoring and management system of water supply in the area. Another water quality-related study was performed by Ahmed et al. [24], where they analyzed the groundwater quality of Najran and found that the water was fit for human use except in a few areas where the groundwater contained higher TDS values.
Many researchers have published work highlighting the causes of water depletion and strategies to minimize its effects. For Saudi Arabia, the availability of water has already been declared the most prioritized issue to be included in sustainability measures [25]. Al-Omran et al. [26] studied the irrigation system under practice in Saudi Arabia in detail and recommended a proper water management system for the conservation of irrigation water. Different techniques have also been published in an attempt to create awareness among the general public to reduce water consumption, as water resources are depleting quickly [27,28,29]. Al-Ansari and Knutsson [30] performed research on the reduction in the water flow of the Tigris and Euphrates Rivers in Iraq, which has caused a decrease in agricultural land during the past 20 years. Srinivasan et al. [31] identified four major factors playing a role in the water crisis, which are changes in the water demand, water supply techniques, governance systems, and infrastructure facilities. Dijk et al. [32] studied the natural and human causes of the Millennium Drought that occurred from 2001 to 2009 in southeast Australia. They concluded that the environmental effect was the major factor for water scarcity in the study area. Wada [33] conducted a related study by modeling groundwater depletion on a global scale and suggested the development of better monitoring and management plans for water use and extraction. Ahmed and Abdelmohsen [34] studied the rates of groundwater depletion and the rate of freshwater recharge to quantify the available amount of water for the Nubian aquifer in Egypt. Mazzoni et al. [35] forecasted the groundwater depletion and water budget deficit for North Africa and the Arabian Peninsula. They concluded that if the current trend of water use and groundwater extraction continues, the countries with the lowest GDP per capita might hit a severe water deficit in the future. In a similar study, Turner et al. [36] predicted the cost analysis of groundwater extraction for the future and concluded that the influence of the cost of groundwater extraction would be huge during the twenty-first century, and their approach shall help in better management of groundwater globally. GIS-based techniques are also in development for the detection of groundwater levels remotely [37]. Few others [38,39,40,41] utilized GIS techniques for evaluating the groundwater depletion rates and the water table level for the USA, the Middle East, on a global scale, and in Saudi Arabia, respectively. Scanlon et al. [38] in another study assessed the effects of groundwater depletion on irrigation in High Plains and Central Valley, USA.
Water scarcity and groundwater quality deterioration are common problems in several regions in Saudi Arabia, and these issues need to be assessed for their influence on public perceptions of water resource conservation and reclamation. The existence of water scarcity conditions effects the domestic and agricultural sectors, resulting in an obstruction to the development effort in the communities where it prevails. Given all the problems related to water resources being faced by the residents of Najran Valley, who are the real stakeholders of Najran Dam, it was found that there is a need for a study to determine the major causes affecting the agricultural activities in the Najran Valley based on the opinion and experience of the actual residents. The following questions were found important to be answered:
  • What are the possible causes of groundwater depletion at Najran Valley?
  • What factors have been involved in affecting agricultural activities?
  • What effects and changes have been observed on the environment and water availability after the construction of the Najran Dam?
  • How do the key stakeholders of Najran Valley perceive the issue of water depletion affecting their daily life and activities?
As there is no such study available, this task was taken up to fill the gap, maintain a record, and keep the data ready whenever needed by the authorities and policymakers. The response to the survey questionnaire was compiled, and all the factors are presented in order of their priority by using statistical analysis techniques. The results of the study presented in this study shall prove to be highly beneficial for the related authorities in making better and timelier decisions to develop better policies regarding the availability of water in the area for domestic or agricultural activities.

2. Methodology of Research and Analysis Options

One of the major dams based on storage capacity in Saudi Arabia is located in Najran Province, and it is named Najran Dam, which is the study area for this research. Najran City is situated in the southwest of the Kingdom near the territorial boundary of Saudi Arabia and Yemen at 17°30′ N and 44°10′ E, having a population of 316,000 with a growth rate of 2.7% [6]. It has varying weather ranging from moderate in summer to cold during winter, with average minimum and maximum temperatures of 6–30 °C. Najran receives a good amount of rainfall during the summer and is considered rich in agriculture [42]. The area has three types of topographical areas. In the west, there are rugged hills, whereas large fields and valleys with slopes lie in the middle of the city, which are useful for farming, and the eastern region consists of deserts, as shown in Figure 3.
Najran Dam, as mentioned in Table 4, is a gravity dam built in 1980 for flood control, domestic and agricultural water supply, and groundwater recharge. The dam has a height of 73 m, and it spans 140 m across the valley, providing a water storage volume of 86 MCM. During the rainy season, it collects the runoff and the sediments to protect the Najran Valley downstream. The water is released, when required, through three spillways [43].
The methodology of the research follows a series of procedures. In the first step, notes were taken after an extensive review of the literature available on the web related to the water resources of Najran Valley. In the second step, a reconnaissance survey was conducted, and basic data were collected from the study site regarding the problems and challenges being faced by the residents related to water resources and agricultural practices being followed after the construction of the Najran Dam. A few professionals in the industry related to water treatment, water supply design, and execution who have hydrological study experience were also consulted to determine the factors affecting the water resources in the region. After compiling the basic information, a few common factors were shortlisted and put down in the form of a questionnaire in the third step. This online questionnaire was designed specifically to obtain the perceptions of the residents of Najran Valley regarding the available water resources and the impact of Najran Dam on agricultural practices. All the required protocols were taken care of while performing the survey. The survey was required to be submitted as “anonymous”, and no identity of any respondent was recorded. The respondents were also given the option of leaving the survey at any time during the response process. Those particular surveys were listed as incomplete and was not included in the statistical analysis. The whole process of data collection and analysis is shown in Figure 4.
The survey questionnaire consisted of two types of questions. The questions of the first type were based on a Likert scale, and the respondents were required to answer on a scale of 1 to 5, representing strongly disagree, disagree, do not know, agree, and strongly agree, respectively. The questions of the second type were given with the options where the respondents were required to select the best suitable option. The format of the online survey questionnaire is shown in Table 5 below.
The responses of all the respondents were compiled on data sheets and categorized based on various factors. The data analysis performed in this research was executed on SPSS Statistics software. The SPSS Statistics software platform offers advanced statistical analysis, a vast library of machine learning algorithms, text analysis, open source extensibility, integration with big data, and seamless deployment into applications [44].
For the first part of the data analysis, the response percentage obtained for all questions was assessed separately, and the factor that received the highest number of selections was considered the highest priority. Along with this, the responses to all questions were compared together as well by using the method of weighted averages (WA). The following Equation (1) was used to calculate the WA of each factor [45]:
A w = R i   n R i
where Aw is the weighted average, Ri is the number of respondents for a specific level n of the Likert scale, and n ranges from 1 to 5.
For further validation and to ensure the reliability of the results, percentile rank (PR) was also obtained for ranking the factors based on their priority or seriousness of the matter. Percentile ranks are found useful when there is a requirement of understanding the value of a score as compared to other scores in the list of frequency distributions. It is a statistical technique that gives the relative standing of a numerical data point when compared to all other data points in a distribution.
The percentile rank was calculated by using the following Equation (2) [45]:
R = f c f 2 n × 100
where R is the percentile rank, fc is the sum of all the scores in the distribution that are less than or equal to the score of interest, f is the frequency of the score of interest, and n is the total number of scores in the distribution.

3. Results and Discussion

A total of 376 people submitted their responses, which included working professionals, researchers, and students living in the Najran Valley. The data regarding the age of the respondents show that almost 72% of the respondents belong to the age group of 30–50 years, as shown in Figure 5.
The respondents between 30–50 years of age comprise a young and experienced class of people who have good insight into the challenges being faced by the Najran Valley regarding the water resources and agriculture. Moreover, the results of statistical analysis are considered to be reliable if the size of the population is at least 30 or more [45]. The greater the size, the higher the reliability. Hence, the acquired responses are considered highly reliable and well-justified, as they exceed 30 by far, and additionally, the proportion of the young group of people is considerably higher among the population. The distribution of the respondents was also analyzed based on their area of residency, as shown in Figure 6, illustrating that 56% of the respondents are residents of the central region of Najran Valley. A few other characteristics of the respondents are shown in Table 6 as well.
A brief discussion is presented in response to all questions one by one. It was noted during the reconnaissance survey that the residents have experienced a reduction in the groundwater valley of the Najran Valley. Question 1 was designed to assess the causes of this groundwater depletion. As shown by the results in Figure 7a, 75% of the residents said that the groundwater depletion has occurred due to the change in climate and precipitation pattern of the area, whereas almost 60% of responses were received in favor of fast population growth and groundwater overuse for agriculture individually; despite the slightly lesser value, these two factors cannot be ruled out. A similar result was obtained for Question 6 as well, as shown in Figure 8, where 43% of the residents again selected the option of lack of precipitation over all other options in response to the greatest threat to the water resources in Najran Valley. The average precipitation reported in Najran is very scarce, with a value of 10–15 mm in March and April only, while the values are even smaller at 5 mm for other months of the year. In addition, UN-Habitat reported in 2019 that the population of Najran City was 319,000, and it is expected to be 500,000 in 2030, with a high growth rate of 2.7% [6], which validates the responses received to these questions.
Question 2 was related to the assessment of factors that have affected the agricultural sector in Najran Valley. The maximum response of 60% was obtained in favor of the option of the preoccupation of commerce and business sectors, as shown in Figure 7b. Furthermore, 54% of the respondents selected the shortage of agricultural land as the major factor. With the advancement of technology and other means of business, many people have diverted their profession from agriculture to other sectors, which has caused the occupation of agricultural land by the business sectors, resulting in a decrease in cultivatable land. This reason is justified by the results received for Question 5 as well, where 48% of the residents said that farmers are now using the latest technology, and most of the irrigation has been shifted to sprinkler and drip systems. The same was reported by Elfeky et al. [46]. Abd El Aal et al. [13], after performing a GIS-based study, noted a decreasing trend in the availability of agricultural land since 2005, which also validates the results obtained for Questions 2 and 5. Another interesting thing to be noted is that the majority of the respondents who indicated the Najran Dam being the main cause for the deterioration of groundwater levels and agricultural activities were from the same segment of the respondents residing downstream of the Najran Valley. The downstream valley is struck badly due to the reduction in runoff, which results in the interruption of groundwater recharge. Moreover, the existence of groundwater wells at a long distance from the dam site makes their recharge from the dam reservoir ineffective and less likely to happen. This is reflected in the results as presented in Figure 7, where about 48% of the respondents for Q1(d) and Q2(e) identified the Najran Dam as responsible for groundwater depletion and the decline of agricultural activities in the region. This situation shows how the conflict of peoples’ interests results in different and conflicting views, which should be taken into account by planners and decisionmakers when developing plans and policies for integrated and sustainable water management for the region.
Question 3 was designed to obtain the opinion of the residents regarding the environmental impacts of the Najran Dam, and 63% of respondents said that due to the sedimentation upstream of the dam, a decrease in the fertility of the soil in the agricultural land downstream has been observed, as shown in Figure 7c. The alteration of a river’s flow and sediment transport downstream of a dam often causes the greatest sustained environmental impacts. The continuous transport of sediments through valley streams is disrupted by the Najran Dam, resulting in sediment deposition upstream of the dam, further resulting in the stoppage of sediments from traveling downstream, which is necessary to maintain channel form and support the riparian ecosystem.
The dam has also stopped the flow of healthy minerals, which are required for the better growth of crops, resulting in a decrease in agricultural production. These results are also validated by the findings of Shahin [47], who performed regression analysis in estimating the flow of sediments through the Najran Dam. Similar results can be obtained by using the methodology of estimating the sediment deposition, which was put forward by Jamil [48].
Positive impacts of the Najran Dam are observed on groundwater wells located upstream of Najran Valley, which is evident with a marked increase in their water levels. However, these positive impacts are limited to the upstream of the valley. In the downstream region, groundwater quality has deteriorated because of limited recharge and continuous deepening of wells to reach deep water layers, which are usually characterized by a high percentage of salt. The results show that the respondents residing downstream of Najran Valley agreed that water salinity and turbidity were one of the major negative impacts of the Najran Dam on their area. This perception is supported by the finding of some studies conducted in the Najran region by JICA [7], which reported that groundwater salinity was found to be increasing particularly with an increase in depth, and the measured dissolved solids in the study area were found in the range of 3000–8000 mL/L.
Similarly, a large number of respondents residing in the upstream part of Najran Valley agreed that the Najran Dam was responsible for the increase in the breeding of harmful insects although the water level in the Najran Reservoir is continuously fluctuating, and water is not kept stagnant for a prolonged period. This result is validated by the common water quality problems currently encountered in the upstream region. The construction of the Najran Dam led to an increase in the levels of groundwater wells, and due to the limited provision of the municipal sewage network in the area, the majority of residents still depend on sewage ditches for disposing of wastewater.
Abdul Salam et al. reported that only about 5% of the residents in the Najran region have access to the municipal sewage network, and the majority of the residents still depends on ditch sewage for their waste disposal [49]. This overlapping and merging of sewage ditches with the groundwater wells have caused water pollution, resulting in the breeding and reproduction of insects and mosquitoes.
Question 4 was related to the effect of the Najran Dam on the floods in the valley, and 77% of the residents agreed that the risk of floods has considerably been reduced in the valley due to the construction of the dam, as shown in Figure 7d. The Najran Dam has a reservoir capacity of almost 8500 hectare-meters, which can store a sufficient amount of water during rainfall season and can keep Najran Valley safe from floods.
For comparison, the responses obtained for Questions 1 to 4 were converted to a weighted average (WA) by using Equation (1) to obtain o the listed factors having the maximum influence, as shown in Figure 9. It can be seen that the WA for a few of the options is peaking as compared to others. These options having the highest WA were rated as the highest priority by the respondents. The highest strength of response was found for Q-4, where people agreed to the fact that the construction of the Najran Dam has reduced the risk of floods that used to happen before the existence of the dam.
For validation of the results obtained through the survey, the percentile rank was calculated for all the factors listed in the questionnaire by using Equation (2). The results of the PR analysis are shown in Table 7 and Figure 10, where factors are now listed as per their ranks.
The data regarding the groundwater level in Al Wajid aquifer in Najran were also compiled to observe the actual situation of water availability [12,50,51,52]. The maximum groundwater level recorded during the years 1980–2020 is shown in Figure 11. Following the trend of the groundwater level over the years, the latter was forecasted for the year 2030, and it was found that if no proper measures are taken in the future, the groundwater level may further reduce to 1120 m above mean sea level, which was recorded as 1124 m above mean sea level during the year 2020. The expected decrease in the groundwater level at Najran is shown as a dotted line in Figure 11.

4. Conclusions and Recommendations

The major factors affecting the water resources and agricultural practices in Najran Valley as perceived by the residents can be summarized as follows:
  • The construction of the Najran Dam has reduced the risk of floods;
  • The major reason for the depletion of the groundwater table at Najran Valley is the change in climate patterns and lack of precipitation;
  • The major environmental effect caused by the construction of the Najran dam is the stoppage of sediments that are required for the fertility of the soil;
  • The preoccupation with commercial and business sectors has affected the agricultural sector of Najran Valley the most.
The changing environment is playing a pivotal role in the depletion of water. Although the Najran Dam has proven to be beneficial against the risk of floods, a proper monitoring and management system must be deployed to efficiently utilize the water stored in the reservoir. Moreover, the recharging of groundwater must also be planned. The sediment-flushing outlets of the dam must also be operated occasionally to release the trapped sediments, which shall help in filling up the Earth’s fissures and also would provide beneficial soil nutrients for better fertility. On the other hand, if Table 4 is read from the bottom, it can be observed that most of the residents still consider agriculture as the major occupation that can stabilize their economy, and they do not consider it a financial liability. In addition, the residents have not observed any considerable issues with soil fertility, as this factor was ranked second last on the list. As the shallow unconfined aquifer is the main source of drinking water in Najran Valley, groundwater protection and quality monitoring are important to prevent negative impacts due to groundwater overexploitation and pollution.
According to the all the major issues regarding water availability in Najran Valley that have been uncovered in this research, the related authorities must reduce the stress on water demand and solve the problems of the residents related to agriculture through efficient management. The housing authorities must ensure new construction that is properly aligned with the available resources of the area. Strong and efficient policies are required to combat the upcoming crisis.

Author Contributions

Conceptualization, S.H.A. and A.A.G.; Methodology, A.A., I.E., T.I.A., R.J. and N.A.A.; Software, R.J.; Validation, I.E., T.I.A. and R.J.; Formal analysis, R.J.; Investigation, A.A. and A.A.G.; Resources, A.A.G. and T.I.A.; Data curation, I.E. and N.A.A.; Writing—original draft, A.A.G. and R.J.; Writing—review & editing, S.H.A., A.A. and N.A.A.; Visualization, T.I.A.; Project administration, S.H.A. and A.A.; Funding acquisition, S.H.A., A.A. and A.A.G. All authors have read and agreed to the published version of the manuscript.

Funding

This research is funded by the Ministry of Education and the Deanship of Scientific Research-Najran University-The Kingdom of Saudi Arabia under code number NU/NRP/SERC/11/3.

Institutional Review Board Statement

The study presented in the article was conducted according to the guidelines of the Declaration of Helsinki and approved by the Ethics Committee of Al-Baha University, Saudi Arabia under Project No. NU/NRP/SERC/11/3.

Informed Consent Statement

It is stated that the personal information of the respondents was not recorded during the questionnaire survey and only their opinion on the subject matter was taken. The survey was distributed online, and the respondents were allowed to keep their identity confidential.

Data Availability Statement

The datasets generated and analyzed during the research are included in the article, and additional data are available for uploading to a repository on demand.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Ghimire, U.; Piman, T.; Shrestha, M.; Aryal, A.; Krittasudthacheewa, C. Assessment of Climate Change Impacts on the Water, Food, and Energy Sectors in Sittaung River Basin, Myanmar. Water 2022, 14, 3434. [Google Scholar] [CrossRef]
  2. Tarroja, B.; AghaKouchak, A.; Samuelsen, S. Quantifying climate change impacts on hydropower generation and implications on electric grid greenhouse gas emissions and operation. Energy 2016, 111, 295–305. [Google Scholar] [CrossRef] [Green Version]
  3. MEWA. Statistics Book 2019: Ministry of Environment Water and Agriculture, Saudi Arabia. 2019. Available online: https://www.mewa.gov.sa/ar/InformationCenter/Researchs/StaticticsData/Pages/default.aspx (accessed on 23 July 2022).
  4. Chowdhury, S.; Al-Zahrani, M. Characterizing water resources and trends of sector wise water consumptions in Saudi Arabia. J. King Saud Univ.-Eng. Sci. 2015, 27, 68–82. [Google Scholar] [CrossRef] [Green Version]
  5. GAS. General Authority of Statistics, Saudi Arabia. 2018. Available online: https://www.stats.gov.sa/en/ (accessed on 23 July 2022).
  6. UN. Najran City Profile 2019, Ministry of Municipal and Rural Affairs and United Nations Human Settlements Program (UN-Habitat). 2019. Available online: https://unhabitat.org/sites/default/files/2020/03/najran.pdf (accessed on 23 July 2022).
  7. JICA. The Study on Master Plan on Renewable Water Resources Development in the Southwest Region in the Kingdom of Saudi Arabia. Final Report, Japan International Cooperation Agency, Yachiyo Engineering Co., Ltd. 2010. Available online: https://openjicareport.jica.go.jp/618/618/618_312_12005757.html (accessed on 15 October 2022).
  8. Al-Ghobari, H.M. The Effect of Chemical Application and Excessive Extraction of Water Resources on Groundwater Quality and Environment in Saudi Arabia Najran Region as Study Case. Water Energy Environ. 2011, 2011, 57. [Google Scholar]
  9. Wikimapia, Najran Valley Dam. 2022. Available online: https://wikimapia.org/34449103/ (accessed on 20 November 2022).
  10. Ghanim, A.A. Water resources crisis in Saudi Arabia, challenges and possible management options: An analytic review. Int. J. Environ. Ecol. Eng. 2019, 13, 51–56. [Google Scholar]
  11. Youssef, A.M.; Sabtan, A.A.; Maerz, N.H.; Zabramawi, Y.A. Earth fissures in wadi najran, kingdom of saudi arabia. Nat. Hazards 2014, 71, 2013–2027. [Google Scholar] [CrossRef]
  12. Alfaifi, H.J.; Kahal, A.Y.; Abdelrahman, K.; Zaidi, F.K.; Albassam, A.; Lashin, A. Assessment of groundwater quality in Southern Saudi Arabia: Case study of Najran area. Arab. J. Geosci. 2020, 13, 101. [Google Scholar] [CrossRef]
  13. Abd El Aal, A.K.; Kamel, M.; Alyami, S.H. Environmental analysis of land use and land change of Najran city: GIS and remote sensing. Arab. J. Sci. Eng. 2020, 45, 8803–8816. [Google Scholar] [CrossRef]
  14. Ormerod, K.J.; Redman, S.; Kelley, S. Public perceptions of potable water reuse, regional growth, and water resources management in the Reno-Sparks area of northern Nevada, USA. City Environ. Interact. 2019, 2, 100015. [Google Scholar] [CrossRef]
  15. Po, M.; Nancarrow, B.E.; Kaercher, J.D. Literature Review of Factors Influencing Public Perceptions of Water Reuse; Land and Water; CSIRO Publishing: Sydney, Australia, 2003; Volume 54. [Google Scholar]
  16. Hua, A.K. Public Perception in Water Resources Development Case Study: Malacca River. Int. J. Humanit. Soc. Sci. Stud. 2015, 2, 78–86. [Google Scholar]
  17. Zhu, Z.; Li, A.; Wang, H. Public perception and acceptability of reclaimed water: The case of Shandong province, China. J. Water Reuse Desalination 2018, 8, 308–330. [Google Scholar] [CrossRef] [Green Version]
  18. McDaniels, T.L.; Axelrod, L.J.; Cavanagh, N. Public perceptions regarding water quality and attitudes toward water conservation in the lower Fraser Basin. Water Resour. Res. 1998, 34, 1299–1306. [Google Scholar] [CrossRef]
  19. Gasmi, F.; Belloumi, M. The Role of The Development Plan in Achieving The Sustainable Development Goals in Najran Region, Saudi Arabia. J. Posit. Sch. Psychol. 2022, 6, 4023–4035. [Google Scholar]
  20. Elkhrachy, I. Flash flood hazard mapping using satellite images and GIS tools: A case study of Najran City, Kingdom of Saudi Arabia (KSA). Egypt. J. Remote Sens. Space Sci. 2015, 18, 261–278. [Google Scholar] [CrossRef]
  21. Elkhrachy, I. Assessment and management flash flood in Najran Wady using GIS and remote sensing. J. Indian Soc. Remote Sens. 2018, 46, 297–308. [Google Scholar] [CrossRef]
  22. Abd El Aal, A.; Kamel, M.; Al-Homidy, A. Using remote sensing and GIS techniques in monitoring and mitigation of geohazards in Najran Region, Saudi Arabia. Geotech. Geol. Eng. 2019, 37, 3673–3700. [Google Scholar] [CrossRef]
  23. Asaad, A.M.; Ahmed, E.M.; Qureshi, M.A.; Alqahtani, J.M. Drinking water quality and public health in Southwestern Saudi Arabia: The need for a national monitoring program. J. Fam. Community Med. 2015, 22, 19. [Google Scholar] [CrossRef] [Green Version]
  24. Ahmed, A.M.; Alwadie, A.; Ibrahim, A.M. Some Aspects of Groundwater Quality in Najran Town, Kigdom of Saudi Arabia. Open Access Libr. J. 2015, 2, e1833. [Google Scholar] [CrossRef]
  25. Shaawat, M.E.; Jamil, R. A guide to environmental building rating system for construction of new buildings in Saudi Arabia. Emir. J. Eng. Res. 2014, 19, 47–56. [Google Scholar]
  26. Al-Omran, A.M.; Al-Khasha, A.; Eslamian, S. Irrigation Water Conservation in Saudi Arabia. In Handbook of Water Harvesting and Conservation: Case Studies and Application Examples; Chapter 25; Wiley Online Library: Hoboken, NJ, USA, 2021. [Google Scholar] [CrossRef]
  27. Jamil, R. Reduction in Fresh Water Consumption by Grey Water Reuse for Flushing and Irrigation: A Case Study of a Multistorey Hotel Building. In Proceedings of the 1st Conference on Sustainability in Civil Engineering, Islamabad, Pakistan, 1 August 2019; pp. 294–300. [Google Scholar]
  28. Musa, A.A. Goal programming model for optimal water allocation of limited resources under increasing demands. Environ. Dev. Sustain. 2021, 23, 5956–5984. [Google Scholar] [CrossRef]
  29. Mallick, J.; Singh, C.K.; AlMesfer, M.K.; Singh, V.P.; Alsubih, M. Groundwater Quality Studies in the Kingdom of Saudi Arabia: Prevalent Research and Management Dimensions. Water 2021, 13, 1266. [Google Scholar] [CrossRef]
  30. Al-Ansari, N.; Knutsson, S. Toward prudent management of water resources in Iraq. J. Adv. Sci. Eng. Res. 2011, 2011, 53–67. [Google Scholar]
  31. Srinivasan, V.; Lambin, E.F.; Gorelick, S.M.; Thompson, B.H.; Rozelle, S. The nature and causes of the global water crisis: Syndromes from a meta-analysis of coupled human-water studies. Water Resour. Res. 2012, 48, W10516. [Google Scholar] [CrossRef]
  32. Van Dijk, A.I.; Beck, H.E.; Crosbie, R.S.; de Jeu, R.A.M.; Liu, Y.Y.; Podger, G.M.; Timbal, B.; Viney, N.R. The Millennium Drought in southeast Australia (2001–2009): Natural and human causes and implications for water resources, ecosystems, economy, and society. Water Resour. Res. 2013, 49, 1040–1057. [Google Scholar] [CrossRef]
  33. Wada, Y. Modeling groundwater depletion at regional and global scales: Present state and future prospects. Surv. Geophys. 2016, 37, 419–451. [Google Scholar] [CrossRef]
  34. Ahmed, M.; Abdelmohsen, K. Quantifying modern recharge and depletion rates of the Nubian Aquifer in Egypt. Surv. Geophys. 2018, 39, 729–751. [Google Scholar] [CrossRef]
  35. Mazzoni, A.; Heggy, E.; Scabbia, G. Forecasting water budget deficits and groundwater depletion in the main fossil aquifer systems in North Africa and the Arabian Peninsula. Glob. Environ. Chang. 2018, 53, 157–173. [Google Scholar] [CrossRef]
  36. Turner, S.W.D.; Hejazi, M.; Yonkofski, C.; Kim, S.H.; Kyle, P. Influence of groundwater extraction costs and resource depletion limits on simulated global nonrenewable water withdrawals over the twenty-first century. Earth’s Future 2019, 7, 123–135. [Google Scholar] [CrossRef] [Green Version]
  37. Jamil, R. GIS-Based Watershed Analysis for Water Storage Facilities in Underdeveloped Areas: Case of a Gravity Hill in Saudi Arabia. In Handbook of Research on Driving Transformational Change in the Digital Built Environment; Chapter 7; IGI Global: Hershey, PA, USA, 2021; pp. 164–178. [Google Scholar]
  38. Scanlon, B.R.; Faunt, C.C.; Longuevergne, L.; Reedy, R.C.; Alley, W.M.; McGuire, V.L.; McMahon, P.B. Groundwater depletion and sustainability of irrigation in the US High Plains and Central Valley. Proc. Natl. Acad. Sci. USA 2012, 109, 9320–9325. [Google Scholar] [CrossRef] [Green Version]
  39. Voss, K.A.; Famiglietti, J.S.; Lo, M.-H.; De Linage, C.; Rodell, M.; Swenson, S.C. Groundwater depletion in the Middle East from GRACE with implications for transboundary water management in the Tigris-Euphrates-Western Iran region. Water Resour. Res. 2013, 49, 904–914. [Google Scholar] [CrossRef] [Green Version]
  40. Döll, P.; Schmied, H.M.; Schuh, C.; Portmann, F.T.; Eicker, A. Global-scale assessment of groundwater depletion and related groundwater abstractions: Combining hydrological modeling with information from well observations and GRACE satellites. Water Resour. Res. 2014, 50, 5698–5720. [Google Scholar] [CrossRef]
  41. Taha, A.I.; Al Deep, M.; Mohamed, A. Investigation of groundwater occurrence using gravity and electrical resistivity methods: A case study from Wadi Sar, Hijaz Mountains, Saudi Arabia. Arab. J. Geosci. 2021, 14, 334. [Google Scholar] [CrossRef]
  42. Chowdhury, S.; Al-Zahrani, M. Water Resources Conservation in Agriculture: Sensitivity Analysis for Climate Change and Growing Seasons. Int. J. Water Resour. Arid Environ. 2016, 5, 109–117. [Google Scholar]
  43. Al-Zahrani, K.H. Sustainable Development of Agriculture and Water Resources in the Kingdom of Saudi Arabia. Conf. Int. J. Arts Sci. 2009, 1, 3–37. [Google Scholar]
  44. SPSS. IBM SPSS Statistics 28 Brief Guide. 2022. Available online: https://www.ibm.com/products/spss-statistics (accessed on 20 November 2022).
  45. Bluman, A. Elementary Statistics—A Step by Step Approach; McGraw-Hill Education: New York, NY, USA, 2014; ISBN 9780073534985. [Google Scholar]
  46. Elfeky, A.; Elfaki, J. A review: Date palm irrigation methods and water resources in the Kingdom of Saudi Arabia. J. Eng. Res. Rep. 2019, 9, 1–11. [Google Scholar] [CrossRef]
  47. Shahin, M. Erosion and Sedimentation in Drainage Basins and in Storage Reservoirs. In Water Resources and Hydrometeorology of the Arab Region; Springer: Berlin/Heidelberg, Germany, 2007; pp. 333–367. [Google Scholar]
  48. Jamil, R. Estimation of sediment deposition at Nausehri reservoir by multiple linear regression and assessment of its effects on reservoir life and power generation capacity. Int. J. Adv. Res. 2015, 1, 46–59. [Google Scholar]
  49. Abdul Salam, A.; Elsegaey, I.; Khraif, R.; Al-Mutairi, A. Population distribution and household conditions in Saudi Arabia: Reflections from the 2010 Census. SpringerPlus 2014, 3, 530. [Google Scholar] [CrossRef]
  50. Al-Kahtani, S.H.; Ismaiel, S.M. Groundwater irrigation management in the Kingdom of Saudi Arabia: A case study of Al-Wajid aquifer. J. US-China Public Adm. 2010, 7, 62. [Google Scholar]
  51. Al-Kahtani, S.H. Optimal Groundwater Irrigation Allocation of Al-Wajid Aquifer in the Kingdom of Saudi Arabia. J. Agric. Sci. Technol. 2011, B1, 735–745. [Google Scholar]
  52. UN-ESCWA and BGR. Wajid Aquifer System. Chapter No. 11. In Inventory of Shared Water Resources in Western Asia; United Nations Publications; United Nations Economic and Social Commission for Western Asia and Bundesanstalt für Geowissenschaften und Rohstoffe: Beirut, Lebanon, 2013; pp. 317–333. ISBN 13: 978-92-1-128361-7. [Google Scholar]
Figure 1. No. of Dams and Percentage Storage Capacity for various Regions of Saudi Arabia [3].
Figure 1. No. of Dams and Percentage Storage Capacity for various Regions of Saudi Arabia [3].
Resources 11 00122 g001
Figure 2. Najran Dam—Upstream and Downstream during Dry Season [9].
Figure 2. Najran Dam—Upstream and Downstream during Dry Season [9].
Resources 11 00122 g002
Figure 3. Satellite Image of the Study Area showing Location of Najran Dam and Najran Valley (Google Earth Pro © 2022 Maxar Technologies, https://www.google.com/intl/en-GB_ALL/permissions/geoguidelines/ accessed on: 13 October 2022).
Figure 3. Satellite Image of the Study Area showing Location of Najran Dam and Najran Valley (Google Earth Pro © 2022 Maxar Technologies, https://www.google.com/intl/en-GB_ALL/permissions/geoguidelines/ accessed on: 13 October 2022).
Resources 11 00122 g003
Figure 4. Methodology and Flow of Research Process.
Figure 4. Methodology and Flow of Research Process.
Resources 11 00122 g004
Figure 5. Age Distribution of Survey Respondents.
Figure 5. Age Distribution of Survey Respondents.
Resources 11 00122 g005
Figure 6. Distribution of Respondents concerning their Location in Najran Valley.
Figure 6. Distribution of Respondents concerning their Location in Najran Valley.
Resources 11 00122 g006
Figure 7. Response Percentage for (a) Question 1, (b) Question 2, (c) Question 3, and (d) Question 4.
Figure 7. Response Percentage for (a) Question 1, (b) Question 2, (c) Question 3, and (d) Question 4.
Resources 11 00122 g007aResources 11 00122 g007b
Figure 8. Response Percentage for Questions 5 and 6.
Figure 8. Response Percentage for Questions 5 and 6.
Resources 11 00122 g008
Figure 9. Weighted Averages for the Response to Questions 1 to 4.
Figure 9. Weighted Averages for the Response to Questions 1 to 4.
Resources 11 00122 g009
Figure 10. Percentile Ranks of Factors Listed in Questionnaire.
Figure 10. Percentile Ranks of Factors Listed in Questionnaire.
Resources 11 00122 g010
Figure 11. Temporal Depletion in Groundwater Level at Najran.
Figure 11. Temporal Depletion in Groundwater Level at Najran.
Resources 11 00122 g011
Table 1. No. of Dams in Saudi Arabia and their Water Storage Capacity [3].
Table 1. No. of Dams in Saudi Arabia and their Water Storage Capacity [3].
RegionNo. of DamsStorage Capacity (MCM)RegionNo. of DamsStorage Capacity (MCM)
Asir117519.5Qassim188.86
Riyadh103106.16Tabuk1615.59
Makkah57861.12Jazan13313.44
Baha4899.06Northern1161.71
Hail4627.8Jouf1014.61
Madinah41112.82Eastern15.5
Najran27103.86
Table 2. Long-Term Mean Monthly Climatic Variables in Najran during the Period 1985–2010 [3].
Table 2. Long-Term Mean Monthly Climatic Variables in Najran during the Period 1985–2010 [3].
MonthJanFebMarAprMayJunJulAugSepOctNovDec
Rainfall (mm)3.41.21719.26.53.52.19.70.151.91
Humidity (%)423432302116171919253341
Temp. (°C)17.520.723.826.530.131.832.932.629.524.521.118
PET (mm/day)4.25.16.36.87.68.67.67.88553.9
Table 3. Amount of Runoff in Najran Valley before Construction of Dam [3].
Table 3. Amount of Runoff in Najran Valley before Construction of Dam [3].
Month1967196819691970197119721973197419751976
Runoff (MCM)3.41.21719.26.53.52.19.70.15
Table 4. Salient Features of Najran Dam [3].
Table 4. Salient Features of Najran Dam [3].
DescriptionDetails
Purpose of DamFlood Control
Type of DamConcrete Gravity
Catchment Area5000 km2
Dam Height73 m
Storage Capacity86 MCM
Reservoir Area5 m2
Length of Spillways69 m
Spillway Discharge Capacity8200 m3/s
Table 5. Survey Questionnaire used for Study.
Table 5. Survey Questionnaire used for Study.
Sr. No.QuestionScale
12345
Q-1In your opinion, what are the possible causes of depletion of groundwater levels in Najran Valley?
aUrban Sprawl
bFast Population Growth
cGroundwater Overuse in Agricultural Activities
dConstruction of Najran Dam
eChange in Climate and Precipitation Pattern
Q-2What factor has played a major role in affecting the agricultural sector of Najran Valley?
aNon-viability of Agriculture Economically
bDecrease in Soil Fertility
cDecrease in Crop Quality
dShortage of Agricultural Land
eNegative Impact of Najran Dam
fPreoccupation with Commerce and Business Sectors
Q-3What type of environmental effect has been observed after the construction of Najran Dam?
aWater Salinity and Turbidity have Increased
bBreeding of Harmful Insects has Increased
cSediments Required for Soil Fertility have Stopped
dEnvironmental Pollution has Increased
Q-4What effect has been observed on floods after the construction of Najran Dam?
aRisk of Flood is Still There
bRisk of Flood has Reduced
Q-5How has the construction of Najran Dam affected the irrigation methods in the valley?
aNo Effect on Method of Irrigation
bIrrigation by Sprinkler and Drip Method has Increased
cIrrigation by Immersion Method has Increased
Q-6What is the reason which poses the greatest threat to the water resources of Najran Valley?
aClimate Change and Lack of Precipitation
bIllegal Sale of Water Using Tankers
cConstruction of Najran Dam
dIncreased Agricultural Activity
eIncreased Number of Groundwater Wells
fLocal Practices and Strict Government Legislation
Table 6. Characteristics of the Respondents.
Table 6. Characteristics of the Respondents.
ParameterCategoriesPercentage
GenderMale68%
Female32%
Marital StatusMarried71%
Unmarried29%
Education LevelPost-Graduate Degree14%
Graduate Degree66%
Diploma7%
Student13%
Employment StatusRetired6%
Employed75%
Unemployed7%
Student12%
Table 7. Percentile Ranks of Factors Listed in Questionnaire.
Table 7. Percentile Ranks of Factors Listed in Questionnaire.
Q. No.Listed FactorRank (R)Percentile (%)
4bRisk of Flood has Reduced1100.0
1eChange in Climate and Precipitation Pattern293.7
3cSediments Required for Soil Fertility have Stopped387.5
3bBreeding of Harmful Insects has Increased481.2
1cGroundwater Overuse in Agricultural Activities575.0
3aWater Salinity and Turbidity have Increased668.7
2fPreoccupation with Commerce and Business Sectors762.5
1bFast Population Growth850.0
4aRisk of Flood is Still There850.0
1dConstruction of Najran Dam1037.5
2dShortage of Agricultural Land1037.5
2eNegative Impact of Najran Dam1231.2
2cDecrease in Crop Quality1325.0
3dEnvironmental Pollution has Increased1418.7
1aUrban Sprawl1512.5
2bDecrease in Soil Fertility166.2
2aNon-viability of Agriculture Economically170.0
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Alyami, S.H.; Alqahtany, A.; Ghanim, A.A.; Elkhrachy, I.; Alrawaf, T.I.; Jamil, R.; Aldossary, N.A. Water Resources Depletion and Its Consequences on Agricultural Activities in Najran Valley. Resources 2022, 11, 122. https://doi.org/10.3390/resources11120122

AMA Style

Alyami SH, Alqahtany A, Ghanim AA, Elkhrachy I, Alrawaf TI, Jamil R, Aldossary NA. Water Resources Depletion and Its Consequences on Agricultural Activities in Najran Valley. Resources. 2022; 11(12):122. https://doi.org/10.3390/resources11120122

Chicago/Turabian Style

Alyami, Saleh H., Ali Alqahtany, Abdulnoor A. Ghanim, Ismail Elkhrachy, Tareq I. Alrawaf, Rehan Jamil, and Naief A. Aldossary. 2022. "Water Resources Depletion and Its Consequences on Agricultural Activities in Najran Valley" Resources 11, no. 12: 122. https://doi.org/10.3390/resources11120122

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop