Next Article in Journal
Strawberry Growth under Current and Future Rainfall Scenarios
Previous Article in Journal
Environmental and Economic Impacts of the Grand Ethiopian Renaissance Dam in Africa
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Understanding Household Water-Use Behavior and Consumption Patterns during COVID-19 Lockdown in Saudi Arabia

by
Abdulaziz I. Almulhim
1,* and
Yusuf A. Aina
2
1
Department of Urban and Regional Planning, College of Architecture and Planning, Imam Abdulrahman Bin Faisal University, P.O. Box 1982, Dammam 31451, Saudi Arabia
2
Department of Geomatics Engineering Technology, Yanbu Industrial College, Yanbu 41912, Saudi Arabia
*
Author to whom correspondence should be addressed.
Water 2022, 14(3), 314; https://doi.org/10.3390/w14030314
Submission received: 16 December 2021 / Revised: 14 January 2022 / Accepted: 18 January 2022 / Published: 20 January 2022
(This article belongs to the Section Water Use and Scarcity)

Abstract

:
With the COVID-19 lockdown impacting the livelihood of people globally, changes in household behaviors, water consumption patterns, etc., have implications on sanitation, hygiene, and disease control. An online questionnaire survey was conducted, and officials were interviewed to assess the impact of the lockdown on water consumption patterns in the Dammam Metropolitan Area, Saudi Arabia. The multiple regression analysis on responses from the survey indicates that water consumption increased by 50% in 86% of the respondents, leading to higher utility bills. Socioeconomic factors also influenced water consumption. The officials interviewed emphasized the need for integrating water policies with disaster management actions. This study contributes to the prospering empirical literature on the pandemic COVID-19 and water consumption/usage behavioral practices by exploring the behavior of household water during COVID-19 in Saudi Arabia. This study can help decision-makers in Saudi Arabia and other developing countries in boosting awareness related to water management in crisis time.

1. Introduction

The coronavirus disease is caused by the novel pathogen SARS-CoV2. The outbreak of the disease began in 2019 in Wuhan, China, and by the mid-summer of 2020, human interactions and human contact soon led to its spread globally [1]. The World Health Organization (WHO) declared the disease a pandemic after it had spread to 114 countries across the world in under three months [2,3]. By the mid of January 2022, the virus had infected over 300 million people worldwide [4]. The COVID-19 pandemic brought out the importance of pure water and hygienic facilities to safeguard the health of humans. The pandemic also drew attention to water insecurities in households around the world [5,6].
The COVID-19 pandemic led to substantial changes in professions and lifestyles across the world as countries enforced minimum travel and socialization [7,8]. Most governments initiated “stay-at-home” orders necessitating businesses not categorized as “important” to limit socialization. Company staff started working from home instead of in offices. Increased unemployment, changes in transportation patterns, and decreased economic activities led to drastic socioeconomic variations [9]. These disturbances in patterns of life and work had a crucial impact on where and how water was consumed during the pandemic [10].
The global community was forced to improve behavioral practices [11,12], such as washing hands with soap and water to enhance hygiene [13]. Sustainable Development Goals (SDGs) 3 and 6 aim to ensure good health, pure water, and proper sanitation. Proper handwashing is addressed in these goals to achieve good health [14]. In order to prevent the spread of COVID-19, the WHO suggested frequent handwashing with soap and water [15]. However, effective handwashing requires easy access to water [16], which is challenging for people in developing countries living in rural districts and areas far from cities [17,18]. They face water scarcity due to high demand and limited supply [19]. Since water supply is crucial, especially amid the pandemic, for people to maintain hygiene [20], high water demand can lead to inadequate water distribution [21]. Therefore, it can be very challenging to run a household without access to a clean and adequate water supply [22].
Access to hygiene infrastructure and clean water decreases the possibility of transmission of COVID-19 by facilitating periodic washing of hands and by decreasing contact with viruses [23,24]. However, about 75% of low- and middle-income households do not have proper facilities for handwashing with soap and water [25], and over half the world’s population lack adequate sanitation [25]. Studies have recently linked SARS-CoV-2 with the dismal census on household water stress in low-income and middle-income nations, especially in regions with a high population in urban slums [26,27,28,29,30].
However, household water insecurity is not confined to developing countries. Highly developed countries such as the United States are also affected by household water insecurity [6,31,32]. The aggregate and general demand peaks of water usage were the focus of research studies and investigations on the effect of COVID-19 on water usage. For example, a notable change was observed in the total demand peak in Germany from 7:10 am (before lockdown) to 9:40 am (over lockdown), changing to weekend patterns [33]. Lüdtke et al. [34] reported about a 14% increase in daily water consumption in northern Germany. According to Marshallsay [35], a 35% increase was observed in the peak daily use in certain areas of the United Kingdom during the lockdown. Investigation data from Brazil revealed that an 11% increase in domestic water usage was observed between 26 days before the lockdown and 26 days during the lockdown [20]. Similarly, Kim et al. [36] highlighted a higher usage of domestic hot water during the COVID-19 lockdown. Although this rise in water consumption is attributed to people staying at home, an increase in preventative measures such as handwashing also contributed to the rise of household water consumption [37]. The increased time people spent at their homes and the consequent changes in behaviors impacted the demand for water in households aggravating ongoing pressure on the network supplying water.
Countries are now faced with the challenge of assuring adequate and clean water supply in the ongoing COVID-19 pandemic [24]. Behavioral changes that can reduce the impact of the pandemic provide can be a source of information to achieve sustainable water supply and production [38,39]. Understanding how measures to control the spread of COVID-19 can affect water usage provides well-grounded facts and data for legislatures to frame policy decisions that can overcome the challenges of water supply in emergencies.
The first case of COVID-19 disease in the Kingdom of Saudi Arabia was reported on 2 March 2020, in the Qatif region, which is in the eastern part of Saudi Arabia. By April 2021, 396,758 confirmed cases were identified, of which 6728 was the number of deaths [40,41]. By the end of March 2020, a complete lockdown was imposed to prevent the spread of the virus. Travel between the different regions of the country was restricted to control the spread of the disease as the main mode of transmission was through droplets from those infected by the virus. Besides the elementary measures of travel restriction by the government of Saudi Arabia, including the ban on travel from one city to another, the Ministry of Health also imposed strict laws to limit outdoor activities, suspending schools, banning prayers in mosques, and minimizing social interactions. The same was imposed in 140 countries across the world to avoid the spread of disease [42,43].
In developing countries such as Saudi Arabia, there is limited research on predictors of variations in water usage under crises such as the COVID-19 pandemic. Countries in the Middle East are already water-scarce regions (<500 m3/capita year1) [44], with Saudi Arabia having a potable groundwater supply of ~30% and a desalinized water supply of ~70%. It is predicted that within 50 years, the groundwater source might be completely depleted. Therefore, there is a great challenge of water provision in Saudi Arabia, and water is rapidly becoming a scarce asset in the nation [45].
This study addresses two main questions: How does water usage vary under the conditions of the COVID-19 pandemic (before and after March 2020)? What characteristics of household-related water usage have increased or decreased under the circumstances of the COVID-19 pandemic (before and after March 2020)? Thus, the main objective of this study is to evaluate how urban water consumption is affected by the spread-prevention action for COVID-19. Understanding the socioeconomic and demographic predictors of variation in household water usage can be used to inform effectual prediction and design interventions for a fair supply of water during times of crisis, such as the COVID-19 pandemic. Investigating the elements that lead to changes in water use during emergency circumstances is important to formulate and execute appropriate policies and interventions for reducing inequality in water distribution during emergencies.

2. Materials and Methods

2.1. Study Area/Setting

Dammam Metropolitan Area (DMA), comprising three major cities, Dammam, Khobar, and Dhahran, is considered a case study in this research (Figure 1). Dammam is the capital of Saudi Arabia’s Eastern Province. It is around 400 km from Riyadh on the Arabian Gulf coast. In 2014, DMA had a population of around 1.66 million, the third-highest in Saudi Arabia [46]. As a global hub for petrochemical refining activities, DMA is a rapidly growing economic center because it influences the global oil market [47]. From a small fishing town in the 1950s, it grew to about 1050 km2 by 2017 [48]. As one of the seven largest cities of the country, it now accommodates around half the country’s population [49]. Water shortages, high water consumption, and poor management are some of the problems in Saudi cities, and the municipality is making all efforts to expand its industrial base for economic growth [50]. Water usage is an important aspect of the city owing to the dry and hot climate. MOMRA [48] highlighted the pressure of water scarcity in Dammam despite sourcing water from desalination plants, which leads to an increase in greenhouse gas emissions.

2.2. Data Collection and Analysis

In this study, two approaches were adopted for data collection to understand the changes in household behavior and water consumption. The first approach involved the administration of questionnaires to residents in the three major cities of DMA. The second approach entailed semi-structured interviews with the officials and policymakers of the water department of DMA. The survey was conducted to investigate the effect of COVID-19 on water usage in DMA households. The questionnaire consisted of four sections: (i) demographic information (residential location, marital status, number of family members, gender, age, nationality), (ii) socioeconomic information (education, employment, household type, income, housing tenure), (iii) water consumption information (working type during the pandemic, change in household water consumption, water bill, type of increase), and (iv) water usage behaviors. Most of the questions in the questionnaire were to be responded on a 5-point Likert scale (strongly agree, agree, neutral, disagree, and strongly disagree), and the remaining included ranking responses, yes/no questions, or neutral options. The questions were in English with Arabic translation included. The questionnaire was pilot tested among the colleagues of the researchers before mailing them to the participants. The feedback from the pilot survey was used to revise and improve the questions.
A cross-sectional survey was applied using QuestionPro (www.questionpro.com, accessed on 1 February 2021) between February and May 2021. This method was preferred since online surveys are quicker, more economical, and anonymous [51]. Snowball sampling method was used to distribute the survey link by email, where the participants shared the link with others in the area through email and WhatsApp groups [52,53,54]. The number of participants reached 810 at the end of three months. According to Cochran’s formula, this number was sufficient for a city with 1.17 million residents and a 0.05 significance level [55]. Participation was voluntary, and the confidentiality of the participants was guaranteed. The snowball sampling method allows studying a society anonymously when the response rate is high [54]. The online survey helped reach a maximum number of participants since distributing the survey to the public, especially female participants, would have been difficult [52,53].
The second approach for collecting data was through interviews conducted with five managers and government officials to investigate key issues in the water policies of DMA during the COVID-19 pandemic. The number of interviewees was limited to five because only senior officials who were knowledgeable about policies and water management issues were chosen. The interviews were conducted via telephone, and the questions were framed in the form of open-ended queries to allow for comprehensive responses. The interview questions were designed to obtain information on the changes in water consumption, the capacity of the water system to meet the increased demand during the lockdown, changes in water policy during the lockdown, and suggestions for revising the water policy.
For data analysis, the statistical package SPSS (version 26) was used to describe the basic features of the data in the study through frequencies and percentages. Pearson’s Chi-squared test (χ2) was used to find the association between the level of increasing water usage behavior and the demographic variables; T-independent sample test and ANOVA test were used to find the mean differences in increasing water usage behavior based on sociodemographic variables and household water consumption. Finally, multiple regression tests were used to identify the predictors of increasing water usage behavior. The independent variables of this study are the socioeconomic variables (education, work organization, income, housing tenure, and housing type) and the dependent variable is the (water usage behavior). The equation for the model of this study would be presented as below:
Y = X1 +X2 + X3−X4 + X5
where;
Y: Water usage behavior;
X1: Education;
X2: Work organization;
X3: Income;
X4: Housing tenure;
X5: Housing type.

2.3. Bias and Limitation

While the survey procedure sought to ensure that the samples represent the population by distributing the questionnaires among different groups in the society, the nature of the survey (online) might introduce a bias towards the educated members of the populace. An attempt was made to cross the 67.3% college degree attainment of the respondents with the degree attainment in DMA. However, the latest data on college degree attainment (23.6% of the population) were national data compiled in 2016 [56]. Efforts have been made by the government since 2015 to improve the proportion of university graduates by increasing foreign university scholarships and local universities. Moreover, recent similar studies reported 72.3% [46] and 84.6% [57] college degree attainment.
One of the limitations of this study is that the problem was mainly investigated through an online questionnaire survey. This was due to limited access to data on water demand and supply. Most previous studies on the impact of the lockdown on water consumption used data from the relevant water supply organization [20,58,59]. In order to quantify the changes in water consumption, the respondents were asked to indicate if there was an increase in their water bills during the lockdown. In Saudi Arabia, the water supply is solely handled by the National Water Company, and the tariff has been 0.027 USD/m3 since 2015 [60]. Therefore, an increase in water bills might indicate an increase in consumption. Moreover, similar studies successfully used online surveys to understand the impact of COVID-19 lockdown on water and energy use [39,61].

3. Results

3.1. Descriptive Analysis of Demographic and Socioeconomic Features

Among the 810 respondents, 424 were male (52.3%), and 386 were female (47.7%). Further, 582 (71.9%) were Saudi citizens, while 228 (28.1%) were expatriates. Most participants (350; 43.2%) were from Dammam, while 285 (35.2%) were from Khobar and 175 (21.6%) were from Dhahran. This is not surprising since Dammam has the highest population in DMA, followed by Khobar, while Dhahran is the least populated region (MOMRA, 2019). A majority of the respondents (567; 70%) were from households with 6 to 10 members. About 387 (47.8%) respondents were married, while 200 (24.7%) were single, and 111 (13.7%) were divorced. Among the respondents, 688 (84.9%) were between the ages of 26 and 65. They were part of the working-class group, implying that most of the population living in DMA were potentially a part of the country’s workforce. Participants under the age of 25 years were 72 (8.9%) in number, and those above 65 were 50 (6.2%).
Table 1 presents the socioeconomic background of the participants, indicating respondents’ education level, the type of organizations they worked for, the total family income, and the kind of housing in which they resided. Family sizes ranged from moderate to large. In general, the participants belonged to the working class, with middle to high income, and homeownership. This population profile has the potential to increase their water consumption during the lockdown since most of them would either not be able to go to work or would work from home. The change from a daily water consumption profile to a weekend water consumption profile due to the stay-at-home rule reflects the spike in water consumption during the lockdown [33].

3.2. Analysis of Household Water Consumption and Water Use Behavior/Patterns

The results of the survey showed that a high percentage (94.9%) of respondents from the total sample (810) worked from home during the lockdown. Likewise, most participants (95.9%) reported an increase in their water consumption during the COVID-19 lockdown. Nearly 86.3% of the respondents reported more than a 50% increase in their water consumption, with the highest percentage of water consumption for kitchen and cooking (82.6%) purposes, followed by hygiene needs (81.7%), watering plants (74%), recreation (swimming pool) (71.5%), and washing vehicles (50.2%). Consequent to the increase in water usage, about 97.2% of the participants affirmed that their water bills were higher during April–May 2020 than April–May 2019 and that the increment in the water bill during April–May 2020 was more than 100 riyals for 75.7% of the respondents. Nevertheless, about 4.1% of the participants reported no change (2.6%) or a decrease (1.5%) in water consumption.
Table 2 and Figure 2 show the overall water use behavior/patterns. The total mean score of 3.65 out of 5 points with a standard deviation of 0.813 corresponded to a high level as per the 5-point Likert scale [62], indicating the high level of water consumption during COVID-19 (Table 2). A breakdown of the results shows that the participants neither considered adopting water-saving measures during the pandemic nor were they willing to adopt it now. The respondents did not reveal much concern regarding the increase in water consumption during the pandemic (Table 2).

3.3. Association between Demographic Features and Water Use Behavior/Patterns

Pearson’s Chi-squared test (χ2) is a statistical test applied to sets of categorical data to test the independence of two variables, expressed in a contingency table. Independence implies that the value of the row variable does not change the probabilities of the column variable (and vice versa) or that the row percentages (or column percentages) remain constant from row to row (or column to column) [63]. Chi-Square results show that there is a statistically significant association between water-use behavior and demographic features (p < 0.01) (See Table 3). Visual display of the results can be seen in Figure 3.
The results reveal that the water-use level of females was significantly higher than that of males; the water use of Saudi citizens was higher than that of expatriates. Dammam respondents used more water than those from Khobar and Dhahran. Respondents who were married participants showed a higher level of water use than those who were not. A family with 6–11 members used more water than those with fewer members. Similarly, young adults between the ages of 36 and 45 showed a propensity to use more water than other age groups. These results provide information for further exploring demographic variables in the interventions to reduce water consumption.

3.4. Differences in Water-Use Behavior Based on Household Water Consumption

From a quick look at the data, it is not possible to determine whether the data samples are independent or dependent, and since there is the need for a statistical difference between the means, a one-way ANOVA test is performed [64]. ANOVA results show that there is a statistically significant difference in water-use behavior based on household water consumption (p < 0.01). Post hoc comparison tests show that this significant difference was found to support working from home, increase in water use, more than 50% increase in water use, higher water bills during April–May 2020 than April–May 2019, and water bill increment of more than 100 riyals (See Table 4 and Figure 4). Therefore, working from home led to significantly different water-use behavior compared with working in essential services and staying at home without working. The differences between those working from home and those at home but not working could be attributed to the schedules that stay-at-home workers must follow to complete their work. While those who were not working might sleep for longer hours, those working could not. That is, longer working hours lead to higher use of water.
A t-test is a type of inferential statistics used widely to demonstrate the difference in the mean of the two groups [65]. T-test results show that there is a statistically significant difference in water-use behavior based on the increasing consumption; the highest mean score of water wastage was for kitchen and cooking by 3.7986, followed by watering the garden by 3.7699, recreation by 3.7614, washing vehicles by 3.7494, and hygiene and shower by 3.7178 (See Table 5 and Figure 5).

3.5. Multiple Regression of Predictors of Increasing Water Usage Behavior

Multiple regression tests were performed to discover the predictors/factors that influence the increase in water-use behavior. The predictor of the dependent variable (DV) is the water use behavior as a continuous variable which out from the overall mean score of the items of water use behavior, which ranged between 1.20 and 5, and the independent variables were education, work organization, income, home type and housing tenure.
A multi-collinearity test was conducted for all regression models. The results revealed that the VIF (the variance inflation factor) for all models was <3 indicating there was no multi-collinearity problem. Further, all models’ residual was normally distributed. Thus, the assumptions for regression analysis were met. The model was well fit (R = 0.413, R Square = 0.170, F = 33.046, p = 0.000 p < 0.05). The results show the significant effect of education, work organization, total family income, and residence type on water-use behavior (Table 6).
The results indicate that those with higher level of education have a tendency to use more water (Beta = 0.062, p = 0.037 *) and the same applies to those whose high family income is high (Beta = 0.282, p = 0.000 **) and have big houses (villas) (Beta= −0.328, p = 0.001 **). Those that are unemployed showed a higher propensity to use more water than the employed. Housing tenure did not have a significant effect on water-use behavior (p > 0.05). Based on the results of multiple regression, the equation for the model would be presented as follow:
Y = 2.491 + 0.062 (X1) + 0.252 (X2) +0.282 (X3)−0.328 (X4) + 0.073(X5)
where,
Y: Water usage behavior (DV Predicted);
X1: Education;
X2: Work organization;
X3: Income;
X4: Housing tenure;
X5: Housing type.
In the interviews that were conducted, the interviewees highlighted the following points in their responses.
i.
Water consumption increased during the lockdown;
ii.
The existing water system needs to be improved to meet emergency demands;
iii.
Government policies were not revised during the lockdown;
iv.
Experts suggest changing the water policy and legislation during crises or emergency lockdown situations by a temporary reduction in consumption tariffs or no disconnection of water supply if payment is delayed;
v.
Some operational faults were also mentioned, such as the reduction in water distributed to customers.

4. Discussion

As per the results and the participant responses, water consumption increased by more than 50% in DMA during the lockdown, with a corresponding increase in utility bills. This buttresses the report by Abu-Bakar et al. [58] that water consumption increased by 46% in England during the lockdown. In another study, the increase in water consumption in households was between 15 and 20% percent, while commercial water consumption decreased by 30–50% [59]. In the GCC, Abulibdeh [66] and Rizvi et al. [67] reported higher usage of water in the residential sector during the COVID-19 lockdown in Qatar and UAE. The percentage increase found in Qatar was a minimum of 9%, depending on the building, either villa or flat. Further, this study revealed that water-use behavior was influenced by both demographic and economic factors. Factors such as gender, nationality, age, house type, employment, and education affected patterns of water consumption. Balacco et al. [68] examined the impact of restrictive measures on demand for water during the lockdown by inspecting the instant flow data of five towns in Apulia, Italy, focusing on user habits. The population water-use behavior and awareness, climate, and the price of the water were found to influence the demand for drinking water.
A significant number of respondents in this study mentioned that they were not ready to adopt water-saving methods. People need to adopt new behavioral patterns to minimize water-related bills related to water. Therefore, it is pertinent to raise awareness on how one can conserve water and at the same time be protected from the virus by regular hand washing. This will also have an impact on service delivery. Policymakers can adopt policies that reward “good behaviour” as highlighted by Ashour et al. [69] and Lusk et al. [6]. The differential tariff already in place can be reviewed to increase the prices for consumptions that are more than the average. A policy should be enacted to aid the deployment of smart water management technologies as part of the smart city initiatives [70]. Above all, citizenship enlightenment and engagement are very important in promoting sustainable consumer behavior.
Understanding the new variations in the use of water during, before, and after the COVID-19 pandemic will help in preparing strategies to improve the supply of water. These strategies are important since the interviewees mentioned instances of operational failures that led to reductions in the water supply. Behavioral practices such as attaining higher education and gaining knowledge about conservation were stated to be correlated with good hygiene practices such as handwashing [71]. Moreover, decision-makers can explore the information on the relationship between the demographic profile and water-use behavior in targeted awareness campaigns and intervention actions.
Apart from the operational failures, the interviewed experts also highlighted the need for system improvement, especially during emergencies. Government interventions in the form of policy changes are essential to reduce the impact of operational failures on the populace. Thus, long- and short-term goals are needed to enhance the supply of water and establish a flexible water system that could reduce the shocks from future emergencies or pandemics. This is crucial in safeguarding the millions living in densely populated cities. With COVID-19 constantly spreading in developing countries where there is no adequate supply of clean water, the population of these areas continues to be highly vulnerable [72]. It has been well-established that in developing countries, there is a lack of adequate supply of water and provision for handwashing [73]. Under such conditions, flexible governance and planning responses are needed to achieve proper management against this shock and its consequences [74].
One of the findings was that working from home is a major factor in increased water consumption during the lockdown. Even the number of respondents reporting washing vehicles is still high despite staying at home. Most people continue to wash their cars since they have already paid for the car to be washed. Moreover, sandstorms in the desert environment can make the car very dirty. People did not travel to work, but they still obtained permission to shop and perform essential tasks. Saudi has a youthful population, and some of them take car washing as recreation. Similarly, recent studies on water demand have clarified the relocation of water usage from public spaces to homes, with high water consumption practices, at the beginning of the COVID-19 pandemic, but this has reduced over time [75]. Several demand strategies rely on existing sociodemographic and socioeconomic household changes and behaviors self-reported through surveys [76,77]. The findings of this study will help draft more accurate interventions and forecasting when enriched with socioeconomic and sociodemographic variables.

5. Conclusions

This paper contributes to the empirical literature on the water consumption/usage behavioral practices associated with the COVID-19 pandemic by exploring the utilization of household water during COVID-19 in the Kingdom of Saudi Arabia. By considering the probable continuation of the threat of the pandemic, it is necessary to understand the preparations made by individuals and the government in terms of essential services that must be available under emergency circumstances. The study findings reveal that the lockdown due to the COVID-19 pandemic had a significant impact on household water consumption behavior influenced by demographic and economic factors. Moreover, there was a reduction in water distribution during the period and a lack of policy interventions to reduce the impacts.
There is a need to incorporate disaster management strategies into water policies to manage public health emergencies, such as the COVID-19 pandemic, in a better way. Antwi et al. [78] highlighted that government intervention and policy in Europe helped to alleviate the impact of the lockdown on water usage. Further studies can investigate the use of water consumption data from the water corporation to validate the water consumption pattern derived from the questionnaire survey.

Author Contributions

Conceptualization, A.I.A. and Y.A.A.; Data curation, A.I.A.; Formal analysis, A.I.A.; Funding acquisition, A.I.A.; Investigation, A.I.A. and Y.A.A.; Methodology, A.I.A. and Y.A.A.; Resources, A.I.A. and Y.A.A.; Visualization, A.I.A.; Writing—original draft, A.I.A. and Y.A.A.; Writing—review and editing, A.I.A. and Y.A.A. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

The first author would like to acknowledge the support from the Deanship of Scientific Research at Imam Abdulrahman Bin Faisal University, Dammam, Saudi Arabia.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Lu, R.; Zhao, X.; Li, J.; Niu, P.; Yang, B.; Wu, H.; Wang, W.; Song, H.; Huang, B.; Zhu, N.; et al. Genomic characterisation and epidemiology of 2019 novel coronavirus: Implications for virus origins and receptor binding. Lancet 2020, 395, 565–574. [Google Scholar] [CrossRef] [Green Version]
  2. Van Bavel, J.J.; Baicker, K.; Boggio, P.S.; Capraro, V.; Cichocka, A.; Cikara, M.; Crockett, M.J.; Crum, A.J.; Douglas, K.M.; Druckman, J.N.; et al. Using social and behavioural science to support COVID-19 pandemic response. Nat. Hum. Behav. 2020, 4, 460–471. [Google Scholar] [CrossRef] [PubMed]
  3. La Rosa, G.; Bonadonna, L.; Lucentini, L.; Kenmoe, S.; Suffredini, E. Coronavirus in water environments: Occurrence, persistence and concentration methods—A scoping review. Water Res. 2020, 179, 115899. [Google Scholar] [CrossRef] [PubMed]
  4. Johns Hopkins University of Medicine. Johns Hopkins Corona Virus Resource Centre. Available online: https://coronavirus.jhu.edu (accessed on 14 January 2022).
  5. Staddon, C.; Everard, M.; Mytton, J.; Octavianti, T.; Powell, W.; Quinn, N.; Uddin, S.M.N.; Young, S.L.; Miller, J.D.; Budds, J.; et al. Water insecurity compounds the global coronavirus crisis. Water Int. 2020, 45, 416–422. [Google Scholar] [CrossRef]
  6. Lusk, M.G.; Krimsky, L.S.; Taylor, N. How COVID-19 Exposed Water Supply Fragility in Florida, USA. Urban Sci. 2021, 5, 90. [Google Scholar] [CrossRef]
  7. Badr, H.S.; Du, H.; Marshall, M.; Dong, E.; Squire, M.M.; Gardner, L.M. Association between mobility patterns and COVID-19 transmission in the USA: A mathematical modelling study. Lancet Infect. Dis. 2020, 20, 1247–1254. [Google Scholar] [CrossRef]
  8. Chen, X.; Qiu, Z. Scenario analysis of non-pharmaceutical interventions on global COVID-19 transmissions. arXiv 2020, arXiv:2004.04529. Available online: http://arxiv.org/abs/2004.04529 (accessed on 11 February 2021).
  9. Engle, S.; Stromme, J.; Zhou, A. Staying at Home: Mobility Effects of COVID-19; SSRN Scholarly Paper ID 3565703; Social Science Research Network: Rochester, NY, USA, 2020. [Google Scholar]
  10. Sowby, R.B. Emergency preparedness after COVID-19: A review of policy statements in the U.S. water sector. Util. Policy 2020, 64, 101058. [Google Scholar] [CrossRef]
  11. Chan, K.W.; Wong, V.T.; Tang, S.C.W. COVID-19: An Update on the Epidemiological, Clinical, Preventive and Therapeutic Evidence and Guidelines of Integrative Chinese–Western Medicine for the Management of 2019 Novel Coronavirus Disease. Am. J. Chin. Med. 2020, 48, 737–762. [Google Scholar] [CrossRef]
  12. Sohrabi, C.; Alsafi, Z.; O’Neill, N.; Khan, M.; Kerwan, A.; Al-Jabir, A.; Iosifidis, C.; Agha, R. World Health Organization declares global emergency: A review of the 2019 novel coronavirus (COVID-19). Int. J. Surg. 2020, 76, 71–76. [Google Scholar] [CrossRef]
  13. UNICEF; WHO. Hand Hygiene for All. Available online: https://www.unicef.org/sites/default/files/2020-06/Handhygiene-for-all-2020_0.pdf (accessed on 11 July 2020).
  14. United Nations Statistical Commission. 2016 Report of the Inter-Agency and Expert Group on Sustainable Development Goal Indicators. Available online: http://ggim.un.org/knowledgebase/KnowledgebaseArticle51479.aspx (accessed on 28 August 2020).
  15. Ekumah, B.; Armah, F.A.; Yawson, D.O.; Quansah, R.; Nyieku, F.E.; Owusu, S.A.; Odoi, J.O.; Afitiri, A.-R. Disparate on-site access to water, sanitation, and food storage heighten the risk of COVID-19 spread in Sub-Saharan Africa. Environ. Res. 2020, 189, 109936. [Google Scholar] [CrossRef] [PubMed]
  16. Pickering, A.J.; Boehm, A.B.; Mwanjali, M.; Davis, J. Efficacy of Waterless Hand Hygiene Compared with Handwashing with Soap: A Field Study in Dar es Salaam, Tanzania. Am. J. Trop. Med. Hyg. 2010, 82, 270–278. [Google Scholar] [CrossRef] [PubMed]
  17. Montgomery, M.A.; Bartram, J.; Elimelech, M. Increasing Functional Sustainability of Water and Sanitation Supplies in Rural Sub-Saharan Africa. Environ. Eng. Sci. 2009, 26, 1017–1023. [Google Scholar] [CrossRef] [Green Version]
  18. Ekane, N.; Nykvist, B.; KjellÉN, M.; Noel, S.; Weitz, N. Multi-level sanitation governance: Understanding and overcoming challenges in the sanitation sector in sub-Saharan Africa. Waterlines 2014, 33, 242–256. [Google Scholar] [CrossRef]
  19. Sahin, O.; Stewart, R.A.; Porter, M.G. Water security through scarcity pricing and reverse osmosis: A system dynamics approach. J. Clean. Prod. 2015, 88, 160–171. [Google Scholar] [CrossRef] [Green Version]
  20. Kalbusch, A.; Henning, E.; Brikalski, M.P.; de Luca, F.V.; Konrath, A.C. Impact of coronavirus (COVID-19) spread-prevention actions on urban water consumption. Resour. Conserv. Recycl. 2020, 163, 105098. [Google Scholar] [CrossRef]
  21. Shang, F.; Uber, J.G.; van Bloemen Waanders, B.G.; Boccelli, D.; Janke, R. Real Time Water Demand Estimation in Water Distribution System. In Proceedings of the Eighth Annual Water Distribution Systems Analysis (WDSA) Symposium, Cincinnati, OH, USA, 27–30 August 2006; pp. 1–14. [Google Scholar] [CrossRef]
  22. Rosinger, A.Y.; Brewis, A.; Wutich, A.; Jepson, W.; Staddon, C.; Stoler, J.; Young, S.L. Water borrowing is consistently practiced globally and is associated with water-related system failures across diverse environments. Glob. Environ. Chang. 2020, 64, 102148. [Google Scholar] [CrossRef]
  23. Alzyood, M.; Jackson, D.; Aveyard, H.; Brooke, J. COVID-19 reinforces the importance of handwashing. J. Clin. Nurs. 2020, 29, 2760–2761. [Google Scholar] [CrossRef]
  24. Brauer, M.; Zhao, J.T.; Bennitt, F.B.; Stanaway, J.D. Global Access to Handwashing: Implications for COVID-19 Control in Low-Income Countries. Environ. Health Perspect. 2020, 128, 057005. [Google Scholar] [CrossRef]
  25. UNICEF; WHO. Progress on Household Drinking Water, Sanitation and Hygiene 2000–2017: Special Focus on Inequalities; UNICEF: New York, NY, USA, 2019; Available online: https://apps.who.int/iris/bitstream/handle/10665/329370/9789241516235-eng.pdf?ua¼1 (accessed on 17 August 2020).
  26. Rafa, N.; Uddin, S.M.N.; Staddon, C. Exploring challenges in safe water availability and accessibility in preventing COVID-19 in refugee settlements. Water Int. 2020, 45, 710–715. [Google Scholar] [CrossRef]
  27. Roy, A.; Basu, A.; Pramanick, K. Water, Sanitation, Hygiene and COVID-19 pandemic: A global socioeconomic analysis. medRxiv 2020. Available online: https://doi.org/10.1101/2020.08.11.20173179 (accessed on 15 March 2021). [CrossRef]
  28. Smiley, S.L.; Agbemor, B.D.; Adams, E.A.; Tutu, R. COVID-19 and water access in Sub-Saharan Africa: Ghana’s free water directive may not benefit water insecure households. Afr. Geogr. Rev. 2020, 39, 398–404. [Google Scholar] [CrossRef]
  29. Stoler, J.; Jepson, W.E.; Wutich, A. Beyond handwashing: Water insecurity undermines COVID-19 response in developing areas. J. Glob. Health 2020, 10, 010355. [Google Scholar] [CrossRef]
  30. Zar, H.J.; Dawa, J.; Fischer, G.B.; Castro-Rodriguez, J.A. Challenges of COVID-19 in children in low- and middle-income countries. Paediatr. Respir. Rev. 2020, 35, 70–74. [Google Scholar] [CrossRef]
  31. Deitz, S.; Meehan, K. Plumbing Poverty: Mapping Hot Spots of Racial and Geographic Inequality in U.S. Household Water Insecurity. Ann. Am. Assoc. Geogr. 2019, 109, 1092–1109. [Google Scholar] [CrossRef]
  32. Riggs, E.; Hughes, J.; Irvin, D.; Leopard, K. An Overview of Clean Water Access Challenges in the United States; UNC Environmetal Finance Center: Chapel Hill, NC, USA, 2017; 32p. [Google Scholar]
  33. Aquatech. Case Study: Data Links COVID-19 Lockdown to Consumption Change. Available online: https://www.aquatechtrade.com/news/utilities/covid-19-lockdowns-impact-water-consumption/ (accessed on 10 July 2020).
  34. Lüdtke, D.U.; Luetkemeier, R.; Schneemann, M.; Liehr, S. Increase in Daily Household Water Demand during the First Wave of the COVID-19 Pandemic in Germany. Water 2021, 13, 260. [Google Scholar] [CrossRef]
  35. Marshallsay, D. The Effect of the Coronavirus Lockdown on Water Use. Available online: https://www.artesia-consulting.co.uk/blog/New%20Waterwise%20article!%20The%20effect%20of%20the%20coronavirus%20lockdown%20on%20water%20use (accessed on 9 December 2020).
  36. Kim, D.; Yim, T.; Lee, J.Y. Analytical study on changes in domestic hot water use caused by COVID-19 pandemic. Energy 2021, 231, 120915. [Google Scholar] [CrossRef]
  37. Jarvis, C.I.; Van Zandvoort, K.; Gimma, A.; Prem, K.; Klepac, P.; Rubin, G.J.; Edmunds, W.J.; CMMID COVID-19 working group. Quantifying the impact of physical distance measures on the transmission of COVID-19 in the UK. BMC Med. 2020, 18, 124. [Google Scholar] [CrossRef]
  38. Sarkis, J.; Cohen, M.J.; Dewick, P.; Schröder, P. A brave new world: Lessons from the COVID-19 pandemic for transitioning to sustainable supply and production. Resour. Conserv. Recycl. 2020, 159, 104894. [Google Scholar] [CrossRef]
  39. Campos, M.A.S.; Carvalho, S.L.; Melo, S.K.; Gonçalves, G.B.F.R.; dos Santos, J.R.; Barros, R.L.; Morgado, U.T.M.A.; da Silva Lopes, E.; Abreu Reis, R.P. Impact of the COVID-19 pandemic on water consumption behaviour. Water Supply 2021, 21, 4058–4067. [Google Scholar] [CrossRef]
  40. Alsofayan, Y.M.; Althunayyan, S.M.; Khan, A.A.; Hakawi, A.M.; Assiri, A.M. Clinical characteristics of COVID-19 in Saudi Arabia: A national retrospective study. J. Infect. Public Health 2020, 13, 920–925. [Google Scholar] [CrossRef]
  41. World Health Organization. Coronavirus Disease (COVID-19) Pandemic. Available online: https://www.who.int/emergencies/diseases/novel-coronavirus-2019 (accessed on 21 May 2020).
  42. Hale, T.; Angrist, N.; Goldszmidt, R.; Kira, B.; Petherick, A.; Philips, T.; Webster, S.; Cameron-Blake, E.; Hallas, L.; Majumdar, S.; et al. A global panel database of pandemic policies (Oxford COVID-19 Government Response Tracker). Nat. Hum. Behav. 2021, 5, 529–538. [Google Scholar] [CrossRef]
  43. Nghiem, L.D.; Morgan, B.; Donner, E.; Short, M.D. The COVID-19 pandemic: Considerations for the waste and wastewater services sector. Case Stud. Chem. Environ. Eng. 2020, 1, 100006. [Google Scholar] [CrossRef]
  44. Al-Saidi, M.; Saliba, S. Water, Energy and Food Supply Security in the Gulf Cooperation Council (GCC) Countries—A Risk Perspective. Water 2019, 11, 455. [Google Scholar] [CrossRef] [Green Version]
  45. Almulhim, A.I.; Aqil, M.; Ahmad, S.; Abdel-Magid, I.M. Sustainable water planning and management research in Saudi Arabia: A data-driven bibliometric analysis. Arab. J. Geosci. 2021, 14, 1950. [Google Scholar] [CrossRef]
  46. AlQahtany, A.M.; Abubakar, I.R. Public perception and attitudes to disaster risks in a coastal metropolis of Saudi Arabia. Int. J. Disaster Risk Reduct. 2020, 44, 101422. [Google Scholar] [CrossRef]
  47. Abubakar, I.R.; Dano, U.L. Sustainable urban planning strategies for mitigating climate change in Saudi Arabia. Environ. Dev. Sustain. 2020, 22, 5129–5152. [Google Scholar] [CrossRef]
  48. MOMRA. Dammam City Profile; MOMRA: Riyadh, Saudi Arabia, 2019. [Google Scholar]
  49. Abubakar, I.R.; Aina, Y.A. Achieving sustainable cities in Saudi Arabia: Juggling the competing urbanization challenges. In E-Planning and Collaboration: Concepts, Methodologies, Tools, and Applications; IGI Global: Hershey, PA, USA, 2018; pp. 234–255. [Google Scholar]
  50. Aina, Y.A.; Wafer, A.; Ahmed, F.; Alshuwaikhat, H.M. Top-down sustainable urban development? Urban governance transformation in Saudi Arabia. Cities 2019, 90, 272–281. [Google Scholar] [CrossRef]
  51. Huang, H.M. Do print and Web surveys provide the same results? Comput. Hum. Behav. 2006, 22, 334–350. [Google Scholar] [CrossRef]
  52. Almulhim, A.I.; Abubakar, I.R. Understanding Public Environmental Awareness and Attitudes toward Circular Economy Transition in Saudi Arabia. Sustainability 2021, 13, 10157. [Google Scholar] [CrossRef]
  53. Almulhim, A. Public Knowledge and Perception of Climate Change and Global Warming in the Context of Environmental Challenges and Policies in Saudi Arabia. In Proceedings of the 15th International Conference on Urban Regeneration and Sustainability, Bilbao, Spain, 5–7 October 2021; WIT Press: Southampton, UK, 2021; pp. 577–589. Available online: https://www.witpress.com/elibrary/wit-transactions-on-ecology-and-the-environment/253/38116 (accessed on 3 January 2022).
  54. Noy, C. Sampling knowledge: The hermeneutics of snowball sampling in qualitative research. Int. J. Soc. Res. Methodol. 2008, 11, 327–344. [Google Scholar] [CrossRef]
  55. Bartlett, J.E., II; Kotrlik, J.W.; Higgins, C.C. Organizational research: Determining appropriate sample size in survey research. Inf. Technol. Learn. Perform. J. 2001, 19, 43–50. [Google Scholar]
  56. Organisation for Economic Co-operation and Development. Education at a Glance 2021; OECD Indicators; OECD Publishing: Paris, France, 2021. [Google Scholar] [CrossRef]
  57. AlQahtany, A. Evaluating the demographic scenario of gated communities in Dammam metropolitan area, Kingdom of Saudi Arabia. Hous. Care Support 2021. ahead-of-print. [Google Scholar] [CrossRef]
  58. Abu-Bakar, H.; Williams, L.; Hallett, S.H. Quantifying the impact of the COVID-19 lockdown on household water consumption patterns in England. npj Clean Water 2021, 4, 1–9. [Google Scholar] [CrossRef]
  59. Cook, J.; Makin, L. COVID Water Use and the Impact on Poverty in the UK. Waterwise and NEA, London. Available online: https://www.nea.org.uk/wp-content/uploads/2020/11/Waterwise-and-NEA-Joint-Paper-November-2020.pdf (accessed on 21 March 2021).
  60. McIlwaine, S.J.; Ouda, O.K. Drivers and challenges to water tariff reform in Saudi Arabia. Int. J. Water Resour. Dev. 2020, 36, 1014–1030. [Google Scholar] [CrossRef]
  61. Huebner, G.M.; Watson, N.E.; Direk, K.; McKenna, E.; Webborn, E.; Hollick, F.; Elam, S.; Oreszczyn, T. Survey study on energy use in UK homes during COVID-19. Build. Cities 2021, 2, 952–969. [Google Scholar] [CrossRef]
  62. Pimentel, J.L. A note on the usage of Likert Scaling for research data analysis. USM R D 2010, 18, 109–112. [Google Scholar]
  63. Plackett, R.L. Karl Pearson and the Chi-Squared Test. Int. Stat. Rev. 1983, 51, 59–72. [Google Scholar] [CrossRef]
  64. González-Rodríguez, G.; Colubi, A.; Gil, M.A. Fuzzy Data treated as functional data: A one-way ANOVA test approach. Comput. Stat. Data Anal. 2012, 56, 943–955. [Google Scholar] [CrossRef]
  65. Ruxton, G.D. The unequal variance t-test is an underused alternative to Student's t-test and the Mann–Whitney U test. Behav. Ecol. 2006, 17, 688–690. [Google Scholar] [CrossRef]
  66. Abulibdeh, A. Spatiotemporal analysis of water-electricity consumption in the context of the COVID-19 pandemic across six socioeconomic sectors in Doha City, Qatar. Appl. Energy 2021, 304, 117864. [Google Scholar] [CrossRef]
  67. Rizvi, S.; Rustum, R.; Deepak, M.; Wright, G.B.; Arthur, S. Identifying and analyzing residential water demand profile; including the impact of COVID-19 and month of Ramadan, for selected developments in Dubai, United Arab Emirates. Water Supply 2021, 21, 1144–1156. [Google Scholar] [CrossRef]
  68. Balacco, G.; Totaro, V.; Iacobellis, V.; Manni, A.; Spagnoletta, M.; Piccinni, A.F. Influence of COVID-19 Spread on Water Drinking Demand: The Case of Puglia Region (Southern Italy). Sustainability 2020, 12, 5919. [Google Scholar] [CrossRef]
  69. Ashour, A.M.; Mohamad, T.I.; Azeem, S.M.; Thomas, S.P.; Aina, Y.A.; Sopian, K.; Ibrahim, A. Deployment of Rooftop Solar Photovoltaic Electrification for Residential Buildings in an Industrial City: A Study on Public Perception and Acceptance. Int. J. Renew. Energy Res. 2021, 11, 945–951. [Google Scholar]
  70. Aina, Y.A. Achieving smart sustainable cities with GeoICT support: The Saudi evolving smart cities. Cities 2017, 71, 49–58. [Google Scholar] [CrossRef]
  71. Nteli, C.; Galanis, P.; Koumpagioti, D.; Poursanidis, G.; Panagiotopoulou, E.; Matziou, V. Assessing the effectiveness of an educational program on compliance with hand hygiene in a pediatric intensive care unit. Adv. Nurs. 2014, 2014, 704232. [Google Scholar] [CrossRef] [Green Version]
  72. Aboelnga, H.T.; Elmahd, A.; Unver, O. OPINION: Coronavirus-Wake-Up Call to Ensure Water and Sanitation for All. Thomson Reuters Foundation News. 26 March 2020. Available online: https://news.trust.org/item/20200326104523-wfz4n/ (accessed on 3 June 2021).
  73. World Health Organisation. WHO Save Lives: Clean Your Hands in the Context of COVID19. Available online: https://www.who.int/docs/default-source/coronaviruse/who-hhcommunity-campaign-finalv3.pdf?sfvrsn¼5f3731ef_2 (accessed on 11 June 2020).
  74. Rodina, L. Planning for water resilience: Competing agendas among Cape Town’s planners and water managers. Environ. Sci. Policy 2019, 99, 10–16. [Google Scholar] [CrossRef]
  75. Vidal, C.; Coronavirus Lockdown Dramatic Changes in Water Consumption, Research Finds. Coronavirus Lockdown Caused Dramatic Changes in Water Consumption, Research Finds. University of Manchester. Available online: https://www.manchester.ac.uk/discover/news/coronavirus-lockdown-caused-dramatic-changes-in-water-consumption/ (accessed on 22 March 2021).
  76. Parker, J.M.; Wilby, R.L. Quantifying Household Water Demand: A Review of Theory and Practice in the UK. Water Resour. Manag. 2013, 27, 981–1011. [Google Scholar] [CrossRef] [Green Version]
  77. Willis, R.; Stewart, R.; Panuwatwanich, K.; Williams, P.; Hollingsworth, A. Quantifying the influence of environmental and water conservation attitudes on household end use water consumption. J. Environ. Manag. 2011, 92, 1996–2009. [Google Scholar] [CrossRef] [Green Version]
  78. Antwi, S.H.; Getty, D.; Linnane, S.; Rolston, A. COVID-19 water sector responses in Europe: A scoping review of preliminary governmental interventions. Sci. Total Environ. 2020, 762, 143068. [Google Scholar] [CrossRef]
Figure 1. Location of Dammam metropolitan area, Saudi Arabia.
Figure 1. Location of Dammam metropolitan area, Saudi Arabia.
Water 14 00314 g001
Figure 2. Water-use behavior patterns.
Figure 2. Water-use behavior patterns.
Water 14 00314 g002
Figure 3. Relationship between behavior patterns and demographic features.
Figure 3. Relationship between behavior patterns and demographic features.
Water 14 00314 g003
Figure 4. Changes in household water consumption.
Figure 4. Changes in household water consumption.
Water 14 00314 g004
Figure 5. Water consumption based on household activities.
Figure 5. Water consumption based on household activities.
Water 14 00314 g005
Table 1. Socioeconomic features.
Table 1. Socioeconomic features.
n%
Level of EducationPrimary or lower506.2
Intermediate769.4
Secondary13917.2
College/university and above54567.3
Which organization do you work for?Government46257.0
Private18723.1
Self-employed728.9
Unemployed8911.0
Total family incomeLess than 5000 SAR *546.7
5000–10,000 SAR10913.5
More than 10,000 SAR64779.9
Residence typeVilla71087.7
Flat10012.3
Housing tenureOwn58171.7
Rented12615.6
Provided by employer728.9
Other313.8
* Note: 1 USD = 3.75 SAR (Saudi Arabian Riyal).
Table 2. Water-use behavior/patterns.
Table 2. Water-use behavior/patterns.
NMinimumMaximumMeanStd. DeviationLevelRank
I did not adopt any water-saving measures during the COVID-19 lockdown810153.831.384High1
I do not consider an increase in water consumption during COVID-19 lockdown as a concern810153.371.501Moderate5
I agree that more water was consumed during the COVID-19 lockdown810153.821.504High2
My electricity bill was higher during the COVID-19 lockdown810153.691.440High3
I do not plan to adopt any measures to reduce water and electricity consumption/bill810153.521.275High4
Water-Use Behavior/Patterns8101.205.003.650.813High
Table 3. Association between demographic features and water-use behavior/patterns.
Table 3. Association between demographic features and water-use behavior/patterns.
Water Use Behavior/PatternsTotal
LowMediumHighChi Squarep-Value
GenderMale26.4%19.6%54.0%100.0%138.9750.000
Female0.0%13.0%87.0%100.0%
NationalitySaudi6.9%12.5%80.6%100.0%126.0180.000
Non-Saudi31.6%26.3%42.1%100.0%
Residential locationDammam7.1%8.6%84.3%100.0%112.3060.000
Khobar27.0%24.9%48.1%100.0%
Dhahran5.7%18.3%76.0%100.0%
Marital statusSingle14.5%15.0%70.5%100.0%30.9110.000
Married6.3%5.4%88.4%100.0%
Divorced8.1%18.0%73.9%100.0%
Widowed17.3%19.9%62.8%100.0%
Resident family membersUnder 520.5%23.5%56.1%100.0%54.9740.000
6–109.2%13.9%76.9%100.0%
11–2029.7%20.7%49.5%100.0%
AgeUnder 2518.3%22.5%59.2%100.0%38.2210.000
26–3515.0%14.5%70.5%100.0%
36–452.0%2.0%96.0%100.0%
46–5517.5%17.5%65.0%100.0%
55–652.6%26.9%70.5%100.0%
66 or more15.3%13.9%70.8%100.0%
Table 4. ANOVA test for differences in water-use behavior based on household water consumption.
Table 4. ANOVA test for differences in water-use behavior based on household water consumption.
NMeanStd. DeviationFSig.
How did you adapt to working during COVID-19?Worked from home7693.68090.7900812.6460.000
Worked in essential service273.11851.02321
Stayed at home without working142.90000.93397
Was there any change in your water consumption during COVID-19?Increase in water use7773.70480.7581854.7090.000
No change212.58100.75075
Decrease in water use121.88331.09032
By what percentage did your water consumption change?Less than 20%182.98890.9664336.1570.000
20–50%713.42250.74185
More than 50%6993.73450.76139
Not sure222.19090.74955
My water bill was higher during April–May 2020 than April–May 2019?Yes7873.69330.7709047.3040.000
Not sure162.25000.72480
No71.82860.72506
Approximate increment in my water bill during April–May 2020:Less than 20 riyals112.80000.9033322.9450.000
20–50 riyals503.33600.76285
51–100 riyals1093.61280.68056
More than 100 riyals6133.74650.77215
Not sure272.49631.03682
Table 5. T-test for significant differences in water-use behavior based on ways in which water usage increases.
Table 5. T-test for significant differences in water-use behavior based on ways in which water usage increases.
Please Tick the Option that Best Describes Your Increased Usage of Water Consumption NMeanStd. Deviationtp-Value
Hygiene and frequent showersNo1483.33920.82203−5.2070.000
Yes6623.71780.79477
Kitchen and cookingNo1413.27270.93909−9.0220.000
Yes6693.79860.73599
Watering the gardenNo2113.30430.84365−7.0580.000
Yes5993.76990.76602
Recreation (swimming pool)No2313.11350.83982−8.2860.000
Yes5793.76140.75138
Washing vehiclesno4033.54690.88933−3.5680.000
yes4073.74940.71569
Table 6. Multiple regression of predictors of increasing water use behavior.
Table 6. Multiple regression of predictors of increasing water use behavior.
ModelUnstandardized CoefficientsStandardized CoefficientstSig.
BStd. ErrorBeta
1(Constant)2.4910.287 8.6920.000
Education0.0620.0300.0682.0870.037
Work organization0.2520.0260.3159.6990.000
Total family income0.2820.0630.1994.4920.000
Residence type−0.3280.101−0.133−3.2380.001
Housing tenure0.0730.0380.0731.9320.054
R = 0.413, R Square = 0.170, F = 33.046, Sig. = 0.000
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Almulhim, A.I.; Aina, Y.A. Understanding Household Water-Use Behavior and Consumption Patterns during COVID-19 Lockdown in Saudi Arabia. Water 2022, 14, 314. https://doi.org/10.3390/w14030314

AMA Style

Almulhim AI, Aina YA. Understanding Household Water-Use Behavior and Consumption Patterns during COVID-19 Lockdown in Saudi Arabia. Water. 2022; 14(3):314. https://doi.org/10.3390/w14030314

Chicago/Turabian Style

Almulhim, Abdulaziz I., and Yusuf A. Aina. 2022. "Understanding Household Water-Use Behavior and Consumption Patterns during COVID-19 Lockdown in Saudi Arabia" Water 14, no. 3: 314. https://doi.org/10.3390/w14030314

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