Skip to main content
International Journal of Environmental Research and Public Health logoLink to International Journal of Environmental Research and Public Health
. 2023 Jan 5;20(2):957. doi: 10.3390/ijerph20020957

COVID-19 and Water Variables: Review and Scientometric Analysis

Roxana Mare 1,*, Codruța Mare 2,3, Adriana Hadarean 1, Anca Hotupan 1, Tania Rus 1
Editor: Paul B Tchounwou
PMCID: PMC9859563  PMID: 36673718

Abstract

COVID-19 has changed the world since 2020, and the field of water specifically, boosting scientific productivity (in terms of published articles). This paper focuses on the influence of COVID-19 on scientific productivity with respect to four water variables: (i) wastewater, (ii) renewable water resources, (iii) freshwater withdrawal, and (iv) access to improved and safe drinking water. The field’s literature was firstly reviewed, and then the maps were built, emphasizing the strong connections between COVID-19 and water-related variables. A total of 94 countries with publications that assess COVID-19 vs. water were considered and evaluated for how they clustered. The final step of the research shows that, on average, scientific productivity on the water topic was mostly conducted in countries with lower COVID-19 infection rates but higher development levels as represented by gross domestic product (GDP) per capita and the human development index (HDI). According to the statistical analysis, the water-related variables are highly significant, with positive coefficients. This validates that countries with higher water-related values conducted more research on the relationship with COVID-19. Wastewater and freshwater withdrawal had the highest impact on the scientific productivity with respect to COVID-19. Access to safe drinking water becomes insignificant in the presence of the development parameters.

Keywords: wastewater, access to improved and safe drinking water, renewable water resources, freshwater withdrawal, scientific productivity, country, GDP per capita, HDI

1. Introduction

Water is both a primary resource for society and the crucial element in the prevention of COVID-19 (by WASH—Water, Sanitation, and Hygiene) [1]. It plays the main role in mitigating the spread of the disease, which is reaching its third pandemic year. As Larson [2] stated in his commentary, almost every infectious disease can be characterized by its relationship to water. This is the main reason why we chose to analyze the connection between this disease that caused a worldwide pandemic starting in 2020 and the interest presented to researchers in the field of water—which equates to the scientific productivity in the water field (in terms of published articles).

The water sector is extremely vast—it includes areas such as potable or freshwater, wastewater, water resources (surface water—rivers, lakes, and groundwater), recreational waters, marine waters, water management, water crises, floods, etc. Researchers tried to assess the relationship between the features of the COVID-19 pandemic and water in the different topics mentioned above.

Water management is the biggest and first factor responsible for the spread of COVID-19 and its eradication. To achieve good water management, especially at these crucial times, it is mandatory to discuss utilities, policies, policy responses, access to safe water for washing and drinking, water consumption, water treatment, water scarcity, and so on. First, each state should consider the human right to water, sanitation, and hygiene (WASH). Authorities must ensure access to safe water and sanitation and even turn to water shutoffs by enforcing water disconnection moratoriums, as in the case of some states in the U.S. [3]. This is an important measure considering increased household consumption during lockdown [4], especially in urban areas [5], and according to different patterns [6]. Unfortunately, not all countries around the world have permanent access to water. Many countries, mostly low-income or developing economies, are still facing water scarcity [7,8,9]. Over 1.6 billion people all over the world face “economic” water scarcity. This is due to a lack of necessary infrastructure [10], the depletion of renewable water resources (30% of the groundwater systems), and the increasing stress on the world’s main aquifers [11]. The quality of renewable water resources is extremely important due to their multiple uses in domestic plants, industrial and agricultural activities, land use, etc. The 2020 lockdown measures offered the possibility for a revival of most rivers and lakes affected by potential malfunctions of wastewater treatment plants (WWTPs) [12], industry—fishing and metals [13], urban pollution [14], agriculture, and land use [15].

Wastewater is a very important water-related variable. It is the first factor capable of providing information related to the disease through its composition. The particles of the COVID-19 enveloped virus can survive in wastewater [16]. Therefore, they need to be first detected in the wastewater [17,18], overseen [19,20,21,22] so they can be predicted [23,24], and then further removed from the wastewater [25,26].

Due to all the aspects presented above and the huge amount of information given by all water research topics, the present paper focuses only on the four most important water-related variables that influence human life and health. These water variables are: (i) wastewater, (ii) renewable water resources, (iii) freshwater withdrawal, and (iv) access to safe and improved drinking water. They are all directly or indirectly influenced by COVID-19. All these five interdependent factors are considered alongside the development parameters: GDP per capita (gross domestic product per capita) and HDI (human development index). The other reason we chose the present study is the lack of a similar kind of study in the literature. Many articles present reviews regarding COVID-19 and different topics related to one or two water topics, such as the WASH perspective in low-income countries [27]; water supply outages [28]; urban and rural water cycles [29]; and detection, survival, and disinfection technologies for COVID-19 [30], but none of them deepen a strict correlation analysis with COVID-19 and the four water variables considered together regarding scientific productivity. Moreover, no control/development parameters, such as GDP per capita and HDI, that express the development level of society were involved in any of the existing scientific papers. As for the bibliometric and scientometric parts, several studies were found, three of which debated the relationship between COVID-19 and scientific productivity in relation to the environment [31,32,33]. Another paper presents further research needs in the field of water, focusing on water-based epidemiology (WBE), WWTPs, the survival and detection of COVID-19 in the water cycle, and aqueous environments [34]. The last scientific paper reported the influence of sewer overflow on public health [35].

The goal of this paper is: (1) to present a critical review of the relationship between: COVID-19, wastewater, renewable water resources, freshwater withdrawal, and access to safe and improved drinking water; (2) to assess how scientific productivity (the number of published articles) in the field of water is determined by the incidence of COVID-19; (3) to assess how scientific productivity is influenced by the incidence of COVID-19 vs. the four most important water-related variables already mentioned above; and (4) to control for the stability of scientific productivity (published articles) vs. COVID-19 vs. the four water variables in the presence of the development level of each country based on GDP per capita and HDI.

The first step in achieving this goal is to create the database according to the scientific papers related to COVID-19 and its family and water found in two of the main important databases—Web of Science (WoS) and Scopus. The next step is to analyze this database according to the maps and networks developed between COVID-19 and water variables. The third step is to evaluate the influence of COVID-19 incidence at the country level upon the scientific productivity in the field of water on the one hand and of produced wastewater, freshwater withdrawal, renewable water resources, and access to safe drinking water on the other. To control for the stability of the results, we introduced the development level proxied by the GDP per capita and the human development index (HDI).

The methodological development of the research is described in Section 2. Section 3 provides a thorough critical review of the relationship between COVID-19 and water-related variables: wastewater, renewable water resources, freshwater withdrawal, and access to improved or safe drinking water, and how all these four topics developed during the COVID-19 pandemic. Section 4 presents and discusses the results of the econometric assessment of how COVID-19 and water-related factors impact scientific productivity in the field, while the last section provides conclusions.

2. Methodology

The scientific productivity of countries with respect to studies assessing the issue of water vs. COVID-19, SARS-CoV-2, and Coronavirus was evaluated using the two most important scientific databases, Web of Science (WoS) and Scopus. The two databases were consulted for articles published up to 2 March 2022, and double counting was avoided to ensure the consistency and quality of the information. A final sample of 853 articles was assessed for this research. The analyzed scientific papers were related to the four water variables considered in this study: (i) wastewater, (ii) renewable water resources, (iii) freshwater withdrawal, and (iv) access to improved or safe drinking water—essential for human health.

2.1. Relation between COVID-19 and Water-Related Variables

All valid results were first introduced in the VOSviewer program, a clustering and mapping tool for network data developed by Van Eck and Waltman [36,37]. This program is used to create and visualize maps and networks of different items: (i) the main keywords related to the aim and variables presented in Table 1 of this paper (the four water variables); and (ii) countries. All data results are analyzed from the point of view of co-occurrences, co-authorship, and links between them. Items are grouped into different clusters; they can contain one or more items, depending on the links and weight attributes of the item included in the network. The higher the weight of the item, the more prominently the item is visualized on the map [36,37]. Clusters located close to each other in the maps indicate close relations. All this mapping related to water variables and their relation to COVID-19 is further completed by a critical review of this part of the water field.

Table 1.

Variables used in the analysis.

Variable Description and Data Source Min Max Mean St. Dev
Dependent
Articles The total number of articles published per country. It represents the number of articles published by authors from a country on the Web of Science (WoS) or Scopus that have specific themes related to water vs. COVID-19. The articles were exhaustively included in the database, avoiding double counting for the ones present in both databases. 1 316 20.89 41.52
Larticles Natural logarithm of Articles. 0 5.76 2.09 1.34
Factors
COVID COVID-19 incidence rate, computed by the authors as the total number of COVID-19 cases/1000 inhabitants in each country based on data provided by worldometers.info/coronavirus on 7 March 2022. 0.077 468.16 138.3 123
LCOVID Natural logarithm of COVID. −2.56 6.15 4.1 1.82
Wastewater “Produced municipal wastewater (109 m3/year). Produced municipal wastewater represents the annual volume of domestic, commercial and industrial effluents, and storm water runoff, generated within urban areas” 1 [38]. 0.0006 7468 83.04 769.9
Lwastewater Natural logarithm of Wastewater −7.42 8.92 −0.29 2.2
Renwres “Total renewable water resources (109 m3/year). Total renewable water resources (TRWR) represent the sum of internal renewable water resources (IRWR) and external renewable water resources (ERWR). It corresponds to the maximum theoretical yearly amount of water available for a country at a given moment” 1 [39]. 0 8647 520.1 1181.86
Lrenwres Natural logarithm of Renwres −2.85 9.06 4.28 2.61
Freshwith “Total freshwater withdrawal (109 m3/year) refers to the sum of surface water withdrawal, that is extracted from rivers, lakes and reservoirs, and groundwater withdrawal extracted from aquifers” 1 [40]. 0.011 647.5 45.15 118.12
Lfreshwith Natural logarithm of Freshwith −4.51 6.47 1.89 2.19
Access “Total population with access to improved or safe drinking water source (%). It represents the percentage of the total population using improved water sources. An “improved” source is one that is likely to provide “safe” water, such as a household connection, a borehole, etc. Current information does not allow yet to establish a relationship between access to safe water and access to improved sources, but WHO and UNICEF are examining this relationship. Safe drinking water is water that contains no biological or chemical pathogen at a level of concentration that is directly harmful to health. This includes treated, untreated, uncontaminated surface water, such as protected boreholes, springs and sanitary wells. The waters of rivers and lakes can only be considered healthy if water quality is regularly monitored and considered acceptable by public health officials. Reasonable access to water means a water supply in the water housing or within a 15-min walk of it” 1 [41]. 30 110 92.16 14.26
Control
HDI “Human Development Index, computed by the United Nations. The Human Development Index (HDI) is a summary measure of average achievement in key dimensions of human development: a long and healthy life, being knowledgeable and have a decent standard of living. The HDI is the geometric mean of normalized indices for each of the three dimensions” 2 [42]. 0.434 0.957 0.790 0.138
GDP_cap “GDP per capita on 30 June 2021, according to World Bank.
GDP per capita is gross domestic product divided by midyear population. GDP is the sum of gross value added by all resident producers in the economy plus any product taxes and minus any subsidies not included in the value of the product. It is calculated without making deductions for depreciation of fabricated assets or for depletion and degradation of natural resources. Data are in current U.S. dollars” 3 [43].
448.6 17,5813.9 21,581.8 26,537.3
LGDPcap Natural logarithm of GDP_cap 6.11 12.08 9.2 1.39

1 Definitions provided by Aquastat, the database of the Food and Agriculture Organization of the United Nations. All data refer to the years 2017 and 2018, the most recent data available around the world. Most of the data have been preserved over time, which is why they can be accepted for the present time too [38,39,40,41]. 2 Definition provided by the United Nations [42]. 3 Definition given by the World Bank [43].

2.2. Statistic Analysis of the Determinants of Scientific Productivity at the Country Level

The second part of the analysis synthesizes all the information from the assessed articles and presents a country-level database with information related to the scientific productivity of countries on the idea of water vs. COVID-19. The entire statistical analysis was performed by using two specialized software programs: Tableau 2021.2 and STATA 15.

The dependent variable in our study is the total number of articles published per country on this topic. A final sample of 94 countries was used in the analysis (see maps in different figures). Variables and descriptive statistics are presented in Table 1.

High variations were depicted in the data through the descriptive analysis, with skewed distributions (Appendix A). Consequently, we transformed the variables using the natural logarithm. This reduces variation, making the distributions closer to the normal one (Appendix B), and allows for the ordinary least squares (OLS) estimation of possible non-linear relationships.

The second step of the analysis consists of cluster analysis. This method was used to group countries based on their features related to the study variables. As a first step, we cluster the countries in the sample based on their scientific productivity and COVID-19 incidence. In the second stage, we also include the water-related variables that we employ. ANOVA values are presented for each cluster stage, along with a description of the average values of the variables for countries in each cluster.

As previously stated, we employed the OLS estimation method to account for the impact of COVID-19 incidence and the water variables on scientific productivity by evaluating the relationship between them. Before the actual estimation, correlations were assessed in order to avoid multicollinearity, while the variance inflation test was applied post-estimation. As the water variables turned out to be highly correlated (Table 2), the OLS models were estimated with COVID-19 and each water variable at a time. Post-estimation tests were applied to check the quality of the models (results of the post-estimation procedures are available upon request). The stability and robustness of the results were addressed in two ways. First, we introduced the level of development proxied by two variables, GDP per cap (a more quantitative proxy) and HDI (a more qualitative proxy), to control for the stability of the relationships. Second, the regression models were tested for heteroskedasticity and afterward estimated in their robust form. The final results based on the robust estimations are presented and interpreted in this study.

Table 2.

Correlation analysis.

LCOVID Lwastewater Lrenwres Lfreshwith Access LGDPcap HDI
LCOVID 1
Lwastewater 0.057 (0.5839) 1
Lrenwres −0.104 (0.322) 0.548 (0.000) 1
Lfreshwith −0.229 (0.027) 0.740 (0.000) 0.661 (0.000) 1
Access 0.622 (0.000) 0.296 (0.004) −0.009 (0.929) 0.120 (0.248) 1
LGDPcap 0.684 (0.000) 0.204 (0.048) −0.167 (0.109) −0.152 (0.143) 0.672 (0.000) 1
HDI 0.751 (0.000) 0.269 (0.009) −0.114 (0.277) −0.036 (0.731) 0.767 (0.000) 0.948 (0.000) 1

Corr. Coef. (p-value).

3. Relationship between COVID-19 and Water-Related Variables

COVID-19 has continued to be the “star” since the world pandemic started at the beginning of 2020, even if more than two years have passed since then, with ups and downs in COVID-19 waves and versions. Alongside COVID-19 and its family (SARS-CoV-2, coronavirus, norovirus, COVID, and so on), the scientific production in the field of water encountered significant and important growth, especially because of the importance of water in the fight against this horrible disease—prevention and detection. Because of this, the four water-related variables—wastewater, renewable water resources, freshwater withdrawal, and access to improved or safe drinking water—are further separately analyzed with respect to their relationships and importance to COVID-19, respectively, and their impact on the scientific productivity in water science.

A general look at the global maps of co-occurrences and links (Figure 1) shows that the core of the maps is COVID-19, which is strongly connected to wastewater (completed by wastewater-based epidemiology and sewage) and water clusters. When discussing water, some of the researchers included everything in this general word, while others, depending on the theme of the papers, took separately the parts of water supply and quality, drinking water, hygiene, and public health, all included in renewable water resources (rivers and surface waters are clearly emphasized, especially in the Scopus map), freshwater withdrawal, and access to improved and safe water.

Figure 1.

Figure 1

Global maps of co-occurrences and links for water and COVID for the two databases—WoS and Scopus.

The greater volume of information on each water variable, such as wastewater, renewable water resources, freshwater withdrawal, and access to improved and safe drinking water, and their interdependence, determines further and deeper analysis of the influence of COVID-19 upon them and scientific productivity. It is inappropriate to analyze only one water-related variable without referring to and linking it to the other three given by the complete circle presented in Figure 2. All water variables are connected between them and further to COVID-19. As stated before, COVID-19 arrives in wastewater in different ways (WASH, urine, feces, etc.). Wastewater contaminates renewable water resources with effluents if the treatment process is not efficient. Water resources are the source for freshwater withdrawal; so, if water resources are infected, the water withdrawn is contaminated too. Therefore, drinking water can also be contaminated, which leads to the continuous spread of COVID-19 disease. Therefore, a vicious circle is created.

Figure 2.

Figure 2

The interdependence of COVID-19 and water-related variables.

3.1. Wastewater

Wastewater is the most important theme and keyword encountered in our research (46% in Web of Science and 55% in Scopus). This has been translated into a great number of articles and a positive impact of wastewater on the scientific productivity linked to the current COVID-19 pandemic. This aspect is further validated by the regression results from Section 4, which clearly position wastewater in the first place regarding its impact on scientific productivity during the COVID-19 pandemic at the country level. The reason is represented by multiple actions that can and have to be taken in the fight against COVID-19, as presented in Table 3.

Table 3.

Actions in the fight against COVID-19.

Actions Methods/Ways References
Detection
  • viral concentration techniques: polyethylene glycol (PEG) precipitation, ultrafiltration, electronegative membrane, ultracentrifugation

  • Sangkham [44]; Torii et al. [45]; Ahmed et al. [46]; Wurtzer et al. [47]

  • Enzyme-linked immunosorbent assay (ELISA)

  • Kilic et al. [48]

  • reverse transcription-polymerase chain reaction (RT-PCR)

  • Ahmed et al. [24]; Heijnen et al. [49]

  • the reverse transcriptase quantitative polymerase chain reaction (RT-qPCR)

  • Yaniv et al. [50]; Chik et al. [51]; Ahmed et al. [52]; Flood et al. [53]; Belhaouari et al. [54]; O’Brien et al. [55]; Hata et al. [56]

  • multiplex RT-qPCR

  • Navarro et al. [57]

  • the reverse transcriptase droplet digital polymerase chain reaction RT-ddPCR

  • Flood et al. [53]

  • next-generation sequencing (NGS), also known as high-throughput sequencing (HTS)

  • Mackul’ak et al. [58]; Hui et al. [59]

  • paper-based diagnostic devices (PADs)

  • Hui et al. [59]

  • nanoscale analytical tools and biosensors

  • Mackul’ak et al. [58]; Yang et al. [60]; Bhalla et al. [61]

  • Rd-Rp based colorimetric reverse transcription loop-mediated isothermal amplification RT-LAMP

  • Haque et al. [62]

Surveillance/monitoring
  • clinical genomic surveillance

  • Nag et al. [63]; Panchal et al. [64]

  • WBE surveillance for variant characterization

  • Nag et al. [63];

  • RT-qPCR

  • Zahedi et al. [65]; Bivins et al. [66]

  • WBE combined with artificial intelligence

  • Randazzo et al. [67]; Abdeldayem et al. [68]

  • WBE based on biosensors

  • Mackul’ak et al. [58]

Recovery of COVID-19 particles
  • Concentrating pipette (CP)

  • Ahmed et al. [69]

  • Adsorption-extraction (AE) method amended with MgCl2

  • Ahmed et al. [69]

  • Ultrafiltration-based methods

  • Flood et al. [53]

  • PEG precipitation

  • Flood et al. [53]

  • Ultracentrifugation

  • Wurtzer et al. [47]

Prevention
  • WBE surveillance was completed by genome sequencing (NGS/HTS) and pathogen for variant characterization

  • Nag et al. [63]; Panchal et al. [64]

  • WBE based on biosensors

  • Mackul’ak et al. [58]

  • Tampon swab and RT-LAMP

  • Bivins et al. [70]

  • RT-qPCR Diagnostic Panel

  • Randazzo et al. [67]

Determination of microbial risks
  • Quantitative assessment

  • Hamadieh et al. [24]

  • Quantitative RT-qPCR

  • Wurtzer et al. [47]; Flood et al. [53]; Hata et al. [56]

Determination of the real number of COVID-19 cases
  • WBE combined with Artificial intelligence and their related Machine learning and Deep learning

  • Ahmed et al. [24]; Abdeldayem et al. [68]

Wastewater is produced in both urban and rural areas, but in most countries, the main wastewater input is given by cities (sewage in rural areas is either absent or very little used). Moreover, Aquastat, the only database that provides full data that is closest to the present and appropriate for further analysis, refers to produced municipal wastewater. Moreover, the research referred to municipal wastewater and sewage [16], especially due to the presence of hospitals in cities [30,71,72,73] and not in rural areas. Zhou et al. [74] confirmed this aspect by presenting a survey on surveillance methods for COVID-19 in wastewater, but only for urban areas (clearly specifying at the end that further studies need to be conducted for peri-urban and rural areas). These are the reasons why the produced municipal wastewater is considered to be the first water variable in the analysis regarding the factors that conditioned the scientific productivity in the field of water during the COVID-19 pandemic. The Scopus map of wastewater co-occurrences in Figure 3 strengthens the approach by illustrating the presence of municipal wastewaters linked to sewage and wastewater in general. Wastewater is the leader of the third most important cluster after COVID-19 and its family in the WoS case, respectively, humans in the Scopus database. This emphasizes the strong relationship between the three most important elements: COVID-19 human infection reflects on wastewater. Sewage, another way of saying wastewater, must not be forgotten either. It is strongly connected with this water variable being included in the same cluster as wastewater (for Scopus) or in the next cluster as importance and dimension (in the WoS case). Sewage is responsible for the transport of the infected water with COVID-19 particles from the source to wastewater treatment plants and for possible further transmission and infection, especially in cases of breakdowns or malfunctions, and for WWTPs workers [75].

Figure 3.

Figure 3

Co-occurrences for wastewater and sewage.

Wastewater is the main route of transmission of COVID-19 disease (as Figure 2 emphasizes) by contamination, which spreads its reach to the other water-related variables analyzed in this paper: water contamination [76], water quality, water purification [77,78,79,80,81], and renewable water resources (surface water and groundwater) [82,83].

3.2. Renewable Water Resources

Renewable water resources are divided into two groups: groundwater and surface water. In both cases, water resources are connected to COVID-19 or/and SARS-CoV-2, wastewater, drinking or tap water, water quality, and access by the population to improved and/or safe drinking water (in the Web of Science, Figure 4) further translates into human health (Scopus database, Figure 4). All these associations are normal and somehow intuitive. Water resources can be contaminated with COVID-19 particles by floods, effluents from WWTPs, fecal-oral transmission, industrial wastewaters, and sewage breakdowns. At the same time, renewable waters represent the sources of drinking water—tap and bottled water. As cleaner the water resources, as smaller the percentage of the spread of COVID-19. Therefore, surface water and groundwater quality are very important regarding scientific productivity during the COVID-19 pandemic. This aspect is also confirmed when discussing water resources and their relationships with the COVID-19 family and human health in the Scopus database (Figure 4). As the determinants will show in Section 4, the more water resources a country has, the more prolific its scientific productivity is.

Figure 4.

Figure 4

Relationships between renewable water resources (surface water and groundwater), water quality, humans, and COVID-19.

Unfortunately, scientific research on groundwater resources emphasizes the diminishing quantity and quality of aquifers [84,85], such as in Nicaragua, for example, especially during the dry season [86]. So, water resources are affected by drought [87,88], rainfall or a lack of it, high temperatures, and increased evaporation, but also by human life and anthropogenic activities [89]. Industry wastewater has the biggest negative contribution to the quality of renewable water resources, followed by agriculture, land use, and commercial and domestic sewage production. To reduce the main polluting factors [85], new methods for pollution control and cleaning, especially of the rivers, were developed based on big data analyses [90], water quality assessment, the water pollution index [91], and magnetic solid-phase extraction (MSPE) [92]. Besides these, limited movement and factory closures led to environmental changes during the COVID-19 lockdown and pandemic [91,93]. All these good changes determined the increase in rainfall and, therefore, the improvement of the stressed aquifers [94]. Even so, considering that world and industry life restarted in 2021, it is of great importance to continuously monitor the changes in aquifers, rivers, and lakes.

3.3. Freshwater Withdrawal

At first glance, freshwater withdrawal appears to have the smallest influence on scientific productivity in the current COVID-19 pandemic when discussing the number of articles on this topic. There are no articles that debate only this topic in relation to COVID-19 (compared to the other water variables), and the percentage of scientific papers included in the database is extremely small (almost 5%). This is also confirmed by the low correlation coefficient of −0.229 in Table 2 between freshwater withdrawal and COVID-19. This means that freshwater is the least affected by COVID-19 (a perfectly normal aspect considering the water is filtered by rock, sand, and ground layers). Practically, according to the life cycle assessment, freshwater withdrawal should be the last option in ensuring the water demand in general [95] and drinking water demand for water savings, respectively.

On the contrary, the analysis of the determinants of scientific productivity at the national level in the presence of the development parameters reveals in, the second highest values for this water variable (a regression coefficient of 0.335, close to 0.366 for wastewater). This highlights the highest influence that freshwater withdrawal has upon the research output in the COVID-19 pandemic, along with wastewater, in the presence of the development parameters.

Freshwater withdrawal is strongly connected to renewable water resources [96,97] (relation strengthened by the highest correlation coefficients from Table 2: 0.661), and drinking water is affected by water insecurity, scarcity, and price [98,99].

3.4. Access to Safe and Improved Drinking Water

The spread of COVID-19 can be stopped by social distancing and the use of water—by washing and drinking safe and improved water provided by renewable water resources. Almost 30% of the global population has access to safe water, which is very low considering the importance of safe water to people’s health. Furthermore, more than 3 billion people lack basic, adequate access to WASH, especially in low- and middle-income countries [100,101,102,103], but this is true even for lower-income classes in high-income countries [11,99]. Of all categories, women and girls are the most vulnerable due to their position according to socio-cultural norms and responsibilities in the family [104]. Therefore, this water-related variable presented a great interest, as confirmed by the significant number of scientific papers published on this topic: 114 in WoS and 134 in Scopus. Safe drinking water is strongly connected to COVID-19 and SARS-CoV-2, an aspect strengthened by the statistical analysis and the results presented in Section 4.2, despite the fact that the World Health Organization indicates that this virus cannot be transmitted through drinking water due to the use of residual chlorine [102]. Water quality is in straight and tight relation to water supply from reservoirs and systems [105]. The quality of tap water is influenced by the change in drinking water demand during the COVID-19 pandemic. Furthermore, drinking water is connected to wastewater and sewage, WASH, and renewable water resources (represented in Figure 5 by surface waters and groundwaters). All these strong relationships are perfectly normal and intuitive. Drinking water can be easily contaminated with COVID-19 particles, especially when drinking it from public spigots, toilets, or any other water channel (i.e., canal) [106]. The correlation analysis from Table 2 also confirms the strongest links between access to improved or safe drinking water and COVID-19 and wastewater, respectively.

Figure 5.

Figure 5

Co-occurrences between water, drinking water, water quality, COVID-19, and the rest of the variables (WoS and Scopus).

Water demand patterns radically changed with the pandemic; household consumption increased all over the world [4,5,6,107,108,109], while industrial and public (universities, colleges, schools, administrative buildings, hotels, etc.) sectors encountered a significant drop in consumption due to their temporary or permanent closures [110,111]. Therefore, the studies are focused on the problems that may occur in the water system infrastructure [112] due to the changes in water demand. Hence, the topics studied were the risks of the degradation of the water quality in buildings’ plumbing (increased levels of lead or copper) and the increased risks of the appearance and growth of bacteria counts (e.g., Legionella) [113,114,115,116,117].

An interesting aspect appears in the relationship between renewable water resources. A strong relationship should be expected between access to safe drinking water and water resources. Unfortunately, the correlation coefficient near zero in Table 2 shows an insignificant connection between the two water-related variables; this aspect is further confirmed in Section 4.2, when introducing the HDI control parameter.

4. Determinants of Scientific Productivity at the Country Level

4.1. Articles vs. COVID-19 Incidence

As we moved the analysis from the article to the country level, it was interesting to see not only the descriptive statistics of the variables (Table 1) but also the geographical positioning of water vs. COVID-19 scientific productivity.

Figure 6 presents:

  • All countries with published articles in the fields of COVID-19 and water;

  • All collaborations between different countries (namely, researchers from different countries) are based on the average number of publications per year in 2020, 2021, and the beginning of 2022. The bigger the bullet, the higher the number of articles and collaborations.

Figure 6.

Figure 6

Figure 6

Countries’ coupling/collaboration based on the average number of publications per year in the WoS and Scopus databases.

If the number of articles published during the three COVID-19 pandemic years is to be discussed, the countries with the greatest number of scientific papers were published mostly in 2021 and less in 2020, not to mention 2022, in which papers were only prevalent at the beginning. This reveals that researchers needed some time to become acquainted with this horrible and lethal disease, COVID-19, and to become accustomed, see what it is about, find ways of fighting against it, and try to see the positives.

In both databases, as seen in Figure 6, the USA is the leader [33] with the highest number of published articles (316). It is somehow to be expected considering its position and influence in the world and the high values for COVID-19 incidence and GDP per cap. All are translated into a higher interest in the topic of COVID-19 and water, more money spent on research, more researchers involved, and more connections with other countries (the USA collaborated with 62 other countries with respect to scientific productivity in the field of water during COVID-19 times, according to Figure 6). The USA (red in Figure 7) is followed by India (orange in Figure 7), China (salmon pink), the UK (salmon pink in Figure 7) (as seen in the Scopus database, Figure 6), and Australia (pink); all are followed by Spain (WoS database) in regards to published articles and country collaborations. The result is validated by Figure 7, which presents only the geographical distribution of the articles at the country level, considering all 94 countries taken into the study. The purple color in Figure 7 shows a small number of articles that decreases once with the color darkening, down to single articles where dark blue-colored countries are concerned.

Figure 7.

Figure 7

Geographical distribution of scientific productivity—articles.

While the USA also had a high COVID-19 incidence [118], it is not even in the top 20. The top five, based on the COVID-19 incidence rate, consists of Denmark, Slovenia, Iceland, Israel, and the Netherlands, with all but the latter two having a very low number of articles published on the topic (three from Denmark, three from Slovenia, and one from Iceland). The maps in Figure 7 and Figure 8 show that we have a mixture of both direct and reverse relationships between the COVID-19 infection rate and the scientific productivity in this field. This is quite interesting, as, logically, we would expect higher scientific productivity in countries with higher COVID-19 incidence rates.

Figure 8.

Figure 8

Geographical distribution of COVID-19 incidence—COVID.

Following the descriptive analysis results, clusters were constructed to see how countries in the sample group stacked up. Articles and COVID were first used as clustering variables and resulted in three clusters (see their components in Figure 9). The USA, UK, India, China, and Australia belong to the same cluster, with high average values for articles and medium for COVID. Table 4 supports the descriptive results. Cluster 3, formed by the above-mentioned countries, is characterized by the highest average center value for articles but middling values for the COVID-19 infection rate. Cluster 1 has the lowest average center value both for articles and for COVID, while Cluster 2 has the highest for COVID.

Figure 9.

Figure 9

Cluster analysis—articles vs. COVID.

Table 4.

Cluster analysis diagnostics and features—articles vs. COVID.

Cluster No. of Countries Centers—Average
Articles COVID
1 61 11.7 67.02
2 28 14.9 293.9
3 5 165.4 136.3
ANOVA
BSS 5.62
WSS 2.41
TSS 8.04

As the goal of our research is related to COVID-19 and water, the water variables were introduced into the analysis. In the first step, the boxplots for each cluster were constructed, and similar behaviors of wastewater, Renwres, and Freshwith (Figure 10) were observed. They all have very small values and variation for cluster 2, medium variation for cluster 1, and very high variation for cluster 3. With respect to Access, the lowest variation is to be found, once again, in cluster 2, with the highest in cluster 1.

Figure 10.

Figure 10

Water variables variation in the clusters based on articles and COVID.

4.2. Articles vs. COVID-19 vs. Water Variables

Finally, the water variables were included in the clustering procedure, and countries were now grouped into four clusters. Similar to the first step, the clustering diagnosis is presented in Table 4, and the clusters on the map are shown in Figure 11. The efficiency of the clustering procedure increases, as the BSS is much higher in the second step. Cluster 4 is made up of only Brazil, which has significantly higher values for wastewater and renewable water resources than any other country in the sample, with 44 articles published on the topic and quite a high COVID incidence (135.06) (Table 5). Cluster 3 is made up of China, India, and the USA, with the highest average center value for articles and high averages for the water variables with respect to the cluster centers. Australia, Argentina, Uruguay, Peru, Lebanon, Jordan, Israel, and most of the European countries belong to the second cluster. They are characterized by medium values for publications in the field, but the highest COVID-19 infection rates and the lowest values for wastewater, Renwres, and Freshwith. However, these countries have the highest access rates to safe-drinking water. The first cluster is made up of the least developed countries, except for a few, such as Canada and Russia. This group has the lowest values for articles and COVID, along with, as expected, the lowest share of the population with access to safe drinking water.

Figure 11.

Figure 11

Cluster analysis—articles vs. COVID vs. water variables.

Table 5.

Cluster analysis diagnostics and features—articles vs. COVID.

Cluster No. of Countries Centers—Average
Articles COVID Wastewater Renwres Freshwith Access
1 49 11.76 47.25 2.32 493.03 31.44 85.5
2 40 18.15 255.4 1.3 135.6 9.07 99.7
3 4 153 83.7 43.2 2665.1 568.9 97.2
4 1 44 135.1 7468 8647 65.7 98.1
ANOVA
BSS 10.84
WSS 5.98
TSS 16.82

The major goal of our analysis is to evaluate whether the COVID-19 incidence and the water resources, wastewater production, freshwater features, or access to safe drinking water of a country impact the scientific production that links water to the current pandemic. The regression results presented in Table 6 clearly show that the influence of the COVID-19 incidence rate on the total number of articles published in this area is significant only when considered along with wastewater and freshwater withdrawal. The impact is positive—studies about the linkage between COVID-19 and water issues were, on average, conducted and mostly published in countries with high infection rates. The correlation analysis has pointed out that more developed countries had higher COVID-19 infection rates, and, usually, these countries have more money spent on research, so, once again, the positive sign is expected.

Table 6.

Robust regression results.

Variables Equation (1) Equation (2) Equation (3) Equation (4)
LCOVID 0.029 (0.051) 0.096 (0.087) 0.159 ** (0.065) −0.13 (0.103)
Lwastewater 0.398 *** (0.073) - - -
Lrenwres - 0.179 ** (0.051) - -
Lfreshwith - - 0.373 *** (0.05) -
Access - - - 0.038 *** (0.013)
Constant 2.09 *** (0.242) 0.961 *** (0.431) 0.737 ** (0.291) −0.9 (0.936)
R 2 0.4305 0.1302 0.3557 0.1073
F (Prob > F) 15.15 (0.000) 7.03 (0.002) 30.92 (0.000) 5.09 (0.008)

Coef. *** followed by (robust std. error); ***, **, * denotes significance at 1%, 5%, and 10%.

It is interesting that the significance of COVID-19 in Equation (3), when considered with freshwater withdrawal, disappears when the two development proxies are introduced in the regressions (Table 7, Equations (3.1) and (3.2)), whereas it becomes highly significant together when considered with renewable resources and access to safe drinking water. However, a very interesting result is actually the sign. In all cases, the coefficient of COVID (first value) is negative (Table 7).

Table 7.

Robust regression results—with control variables.

Variables Equation (1.1) Equation (1.2) Equation (2.1) Equation (2.2) Equation (3.1) Equation (3.2) Equation (4.1) Equation (4.2)
LCOVID −0.128 * (0.066) −0.128 (0.084) −0.219 *** (0.068) −0.252 *** (0.081) −0.092 (0.072) −0.085 (0.099) −0.253 ** (0.099) −0.285 ** (0.076)
Lwastewater 0.366 *** (0.071) 0.358 *** (0.072) - - - - - -
Lrenwres - - 0.211 *** (0.041) 0.191 *** (0.044) - - - -
Lfreshwith - - - - 0.371 *** (0.05) 0.335 *** (0.053) - -
Access - - - - - - 0.024 * (0.013) 0.016 (0.014)
LGDPcap 0.305 *** (0.112) - 0.627 *** (0.112) - 0.480 *** (0.103) - 0.373 ** (0.167) -
HDI - 2.82 ** (1.262) - 6.176 *** (1.161) - 4.123 *** (1.248) - 4.608 ** (1.976)
Constant −0.083 (0.883) 0.494 (0.762) −3.64 *** (0.917) −2.546 ** (0.733) −2.649 *** (0.768) −1.451 ** (0.661) −2.48 ** (1.09) −1.899 ** (0.880)
R 2 0.4809 0.4628 0.3471 0.3096 0.4872 0.4304 0.1718 0.1721
F (Prob > F) 12.32 (0.000) 13.24 (0.000) 18.62 (0.000) 7.43 (0.000) 6.04 (0.000) 23.38 (0.000) 6.01 (0.000) 6.74 (0.000)

Coef. *** (robust std. error); ***, **, * denotes significance at 1%, 5%, 10%.

Since the main goal of introducing the development proxies is to assess the stability of the relationship between scientific productivity in the field and COVID, on the one hand, and water variables, on the other, we can conclude that the relationship between COVID-19 infection rates and articles is not stable. This is somewhat shown by the second cluster analysis (Figure 11 and Table 5). We can see that the resulting clusters do not have the same behavior for all variables, just as described in the related part of the article.

The highest impact of COVID-19 on the research output appears in the models with access (Equations (4.1) and (4.2)).

With regard to the impact of water-related variables, it can be seen that their influence is positive and highly significant in all model specifications, with the exception of access to safe drinking water, which becomes insignificant when the development level is controlled for through the HDI. With respect to the control variables, just as expected, they have positive coefficients—higher scientific productivity with respect to water vs. COVID-19 is present in more developed countries. This can be explained by the fact that such countries have better research infrastructure and more money devoted to research and development. Both the GDP per cap and HDI are highly significant in all models.

Consequently, we can conclude that scientific production related to water vs. the pandemic was more prolific in countries with higher wastewater production, more renewable water resources, more freshwater withdrawal, and a higher share of the population with access to improved or safe drinking water. The USA is the leader, as stated before; India, China, and the UK complete the top four (as the number of published articles decreases from 316 for the USA to 130 for the UK). The ranking is almost the same as the one made at the beginning of 2021, even if more than one year of COVID-19 has passed since then. Important differences appear in the number of articles, which was significantly higher in 2022, and the exact order of each country on top, depending on the researched area [32,34]. Wastewater and freshwater withdrawal have the highest impact on scientific productivity (in the simple models in Table 5 and Table 6, with control variables in Table 7 too). Both variables have very similar coefficients of almost 0.4 (0.398 for wastewater and 0.373 for freshwater withdrawal) compared to the other two variables that reached low and very low coefficients (only 0.038 for access to safe and improved drinking water). On average, countries with higher values for these variables had higher scientific productivity. These results are also validated by the numbers given by the Aquastat database linked with the numbers of articles from our database: the USA is the first on top with an amount of 60.41 × 109 m3/year of produced municipal wastewater. The USA is the leader in wastewater articles, with a total of 125 on this topic alone. A deviation appears in the cases of India and China. India comes in second, with 47 scientific papers, even if the produced wastewater is only 15.45 × 109 m3/year, compared to China, which produces the second-highest amount of wastewater (48.51 × 109 m3/year) and has only 34 papers on wastewater. Lastly is the UK, with a total of 37 articles on wastewater and 4.089 × 109 m3/year of wastewater produced [38,39,40,41]. The highly impactful effect of wastewater is also emphasized in the density map in Figure 12 (VOSviewer).

Figure 12.

Figure 12

Density visualization map of the strongest relationship between COVID-19 and wastewater.

When discussing freshwater withdrawal, Figure 13 presents the correlation between the scientific productivity at the country level for the top four countries and the data provided by Aquastat for this water variable [38,39,40,41]. India and China are the leaders in freshwater withdrawal, but with a significantly lower number of published articles compared to the USA. Of course, countries’ populations and surfaces must not be forgotten. Moreover, an important aspect is the life cycle assessment process and people’s awareness of saving water and naturally renewable resources. The lowest value of the total freshwater withdrawal for the UK shows this awareness of water savings among the English people (when freshwater withdrawal should be the last option). With all these, the UK has the same scientific productivity as China (which has a freshwater withdrawal value 70 times greater than the UK).

Figure 13.

Figure 13

Correlation between scientific productivity and freshwater withdrawal for the top four countries.

5. Conclusions

The highest number of published articles (in terms of the highest scientific productivity) between the beginning of the COVID-19 era, from the 2020s to 2 March 2022, in the Web of Science (WoS) and Scopus scientific databases confirm the interest in this topic of COVID-19 and water field. The literature review conducted emphasizes the high co-occurrence and interdependence of the terms COVID-19 and water-related variables: (i) wastewater, (ii) renewable water resources, (iii) freshwater withdrawal, and (iv) access to improved and safe drinking water. The interconnection of the relationships between water variables and COVID-19 disease is confirmed or rebutted by the control/development parameters: GDP per capita, and HDI. It is interesting to see how much and in what ways they influenced scientific productivity.

It was expected that countries with a higher COVID-19 incidence would be more interested in water management related to this disease and conduct more research. However, in fact, the situation is not quite the same. The USA, India, and the UK researched and published a lot on the subject but had medium COVID-19 rates. Interesting is the fact that countries with high COVID-19 rates (the top five) had low publication performance with respect to the water topic and vice versa. The research on water vs. COVID-19 was mostly conducted in countries with high values for the water-related variables that we considered, regardless of whether we used freshwater withdrawal with resources or wastewater. We can thus conclude that countries with more water resources, better access to water, and better wastewater management were more interested in finding out how they could manage the water issue at the time of the pandemic. The relationships remain stable in the presence of the control factors related to the development level. The latter group of variables also has a direct effect on scientific productivity. The relationship is not surprising, as more developed countries have more money devoted to research and a far better research infrastructure. With all these, the topic of COVID-19 and water still needs further research, since water secures our lives, health, and needs.

Appendix A. Histogram of the Dependent Variable—Articles

graphic file with name ijerph-20-00957-i001.jpg

Appendix B. Histogram of the Logarithmic Transformation of the Dependent Variable—Larticles

graphic file with name ijerph-20-00957-i002.jpg

Author Contributions

Conceptualization, R.M., C.M. and A.H. (Adriana Hadarean); methodology, R.M. and C.M.; software, R.M. and C.M.; validation, R.M., C.M. and A.H. (Adriana Hadarean); formal analysis, R.M. and C.M.; investigation, R.M., C.M., A.H. (Adriana Hadarean), A.H. (Anca Hotupan) and T.R.; resources, R.M., C.M. and T.R.; data curation, R.M. and C.M.; writing—original draft preparation, R.M., C.M. and A.H. (Adriana Hadarean); writing—review and editing, R.M., C.M., A.H. (Adriana Hadarean), A.H. (Anca Hotupan) and T.R.; visualization, R.M. and C.M.; supervision, R.M., C.M., A.H. (Adriana Hadarean) and T.R. All authors have read and agreed to the published version of the manuscript.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

Funding Statement

This research received no external funding.

Footnotes

Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

References

  • 1.World Health Organization . Water, Sanitation, Hygiene and Waste Management for SARS-CoV-2, the Virus That Causes COVID-19: Interim Guidance. WHO; Geneva, Switzerland: 2020. WHO/2019-nCoV/IPC_WASH/2020.4. [Google Scholar]
  • 2.Larson R. Water law and the response to COVID-19. Water Int. 2020;45:716–721. doi: 10.1080/02508060.2020.1835422. [DOI] [Google Scholar]
  • 3.Warner M.E., Zhang X., Rivas M.G. Which states and cities protect residents from water shutoffs in the COVID-19 pandemic? Util. Policy. 2020;67:101118. doi: 10.1016/j.jup.2020.101118. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 4.Ludtke 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. doi: 10.3390/w13030260. [DOI] [Google Scholar]
  • 5.Kalbusch A., Henning E., Brikalski M.P., deLuca F.V., Konrath A.C. Impact of coronavirus (COVID-19) spread-prevention actions on urban water consumption. Resour. Conserv. Recycl. 2020;163:105098. doi: 10.1016/j.resconrec.2020.105098. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 6.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;4:13. doi: 10.1038/s41545-021-00103-8. [DOI] [Google Scholar]
  • 7.Anim D.O., Ofori-Asenso R. Letter to the editor: Water scarcity and COVID-19 in sub-Saharan Africa. J. Infect. 2020;81:e108–e109. doi: 10.1016/j.jinf.2020.05.032. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 8.Jiwani S.S., Antiporta D.A. Inequalities in access to water and soap matter for the COVID-19 response in sub-Saharan Africa. Int. J. Equity Health. 2020;19:82. doi: 10.1186/s12939-020-01199-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9.Zvobgo L., Do P. COVID-19 and the call for ‘Safe Hands’: Challenges facing the under-resourced municipalities that lack potable water access—A case study of Chitungwiza municipality, Zimbabwe. Water Res. X. 2020;9:100074. doi: 10.1016/j.wroa.2020.100074. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 10.Paplorey C. The impact of the COVID-19 health crisis on the water cycle in France (L’impact de la crise sanitaire du COVID-19 sur le cycle de l’eau en France) La Houille Blanche. 2020;82:8. doi: 10.1051/lhb/2020031. [DOI] [Google Scholar]
  • 11.UNESCO The United Nations World Water Development Report 2021: Valuing Water. 2021. [(accessed on 7 March 2022)]. Available online: https://unesdoc.unesco.org/ark:/48223/pf0000375724.
  • 12.Haramoto E., Malla B., Thakali O., Kitajima M. First environmental surveillance for the presence of SARS-CoV-2 RNA in wastewater and river water in Japan. Sci. Total Environ. 2020;737:140405. doi: 10.1016/j.scitotenv.2020.140405. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 13.Selvam S., Jesuraja K., Venkatramanan S., Chung S.Y., Roy P.D., Muthukumar P., Kumar M. Imprints of pandemic lockdown on subsurface water quality in the coastal industrial city of Tuticorin, South India: A revival perspective. Sci. Total Environ. 2020;738:139848. doi: 10.1016/j.scitotenv.2020.139848. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 14.Muduli P.R., Kumar A., Kanuri V.V., Mishra D.R., Acharya P., Saha R., Biswas M.K., Vidyarthi A.K., Sudhakar A. Water quality assessment of the Ganges River during COVID-19 lockdown. Int. J. Environ. Sci. Technol. 2021;18:1645–1652. doi: 10.1007/s13762-021-03245-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 15.Molekoa M.D., Avtar R., Kumar P., Thu Minh H.V., Dasgupta R., Johnson B.A., Sahu N., Verma R.L., Yunus A.P. Spatio-Temporal Analysis of Surface Water Quality in Mokopane Area, Limpopo, South Africa. Water. 2021;13:220. doi: 10.3390/w13020220. [DOI] [Google Scholar]
  • 16.Baldovin T., Amoruso I., Fonzo M., Buja A., Baldo V., Cocchio S., Bertoncello C. SARS-CoV-2 RNA detection and persistence in wastewater samples: An experimental network for COVID-19 environmental surveillance in Padua, Veneto Region (NE Italy) Sci. Total Environ. 2021;760:143329. doi: 10.1016/j.scitotenv.2020.143329. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17.Sherchan S.P., Shahin S., Ward S., Tandukar S., Aw T.G., Schmitz B., Ahmed W., Kitajima M. First detection of SARS-CoV-2 RNA in wastewater in North America: A study in Louisiana, USA. Sci. Total Environ. 2020;743:140621. doi: 10.1016/j.scitotenv.2020.140621. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18.Westhaus S., Weber F.A., Schiwy S., Linnemann V., Brinkmanne M., Widera M., Greve C., Janke A., Hollert H., Wintgens T., et al. Detection of SARS-CoV-2 in raw and treated wastewater in Germany—Suitability for COVID-19 surveillance and potential transmission risks. Sci. Total Environ. 2021;751:141750. doi: 10.1016/j.scitotenv.2020.141750. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Arora S., Nag A., Sethi J., Rajvanshi J., Saxena S., Shrivastava S.K., Gupta A.B. Sewage surveillance for the presence of SARS-CoV-2 genome as a useful wastewater based epidemiology (WBE) tracking tool in India. Water Sci. Technol. 2020;82:2823–2836. doi: 10.2166/wst.2020.540. [DOI] [PubMed] [Google Scholar]
  • 20.Kitajima M., Ahmed W., Bibby K., Carducci A., Gerba C.P., Hamilton K.A., Haramoto E., Rose J.B. SARS-CoV-2 in wastewater: State of the knowledge and research needs. Sci. Total Environ. 2020;739:139076. doi: 10.1016/j.scitotenv.2020.139076. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21.Larsen D.A., Wigginton K.R. Tracking COVID-19 with wastewater. Nat. Biotechnol. 2020;38:1151–1153. doi: 10.1038/s41587-020-0690-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 22.Tiwari S.B., Gahlot P., Tyagi V.K., Zhang L., Zhou Y., Kazmi A.A., Kumar M. Surveillance of Wastewater for Early Epidemic Prediction (SWEEP): Environmental and health security perspectives in the post COVID-19 Anthropocene. Environ. Res. 2021;195:110831. doi: 10.1016/j.envres.2021.110831. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 23.Hamadieh Z., Hamilton K., Silverman A. Systematic review of the relative concentrations of noroviruses and fecal indicator bacteria in wastewater: Considerations for use in quantitative microbial risk assessment. J. Water Health. 2021;19:918–932. doi: 10.2166/wh.2021.068. [DOI] [PubMed] [Google Scholar]
  • 24.Ahmed W., Bivins A., Simpson S.L., Bertsch P.M., Ehret J., Hosegood I., Metcalfe S.S., Smith W.J.M., Thomas K.V., Tynan J., et al. Wastewater surveillance demonstrates high predictive value for COVID-19 infection on board repatriation flights to Australia. Environ. Int. 2022;158:106938. doi: 10.1016/j.envint.2021.106938. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 25.Saawarm B., Hait S. Occurrence, fate and removal of SARS-CoV-2 in wastewater: Current knowledge and future perspectives. J. Environ. Chem. Eng. 2021;9:104870. doi: 10.1016/j.jece.2020.104870. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 26.Cuevas-Ferrando E., Perez-Cataluna A., Allende A., Guix S., Randazzo W., Sanchez G. Recovering coronavirus from large volumes of water. Sci. Total Environ. 2021;762:143101. doi: 10.1016/j.scitotenv.2020.143101. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 27.Gwenzi W. Leaving no stone unturned in light of the COVID-19 faecal-oral hypothesis? A water, sanitation and hygiene (WASH) perspective targeting low-income countries. Sci. Total Environ. 2021;753:141751. doi: 10.1016/j.scitotenv.2020.141751. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 28.Sanger N., Heinzel C., Sandholz S. Advancing resilience of critical health infrastructures to cascading impacts of water supply outages–insights from a systematic literature review. Infrastructures. 2021;6:177. doi: 10.3390/infrastructures6120177. [DOI] [Google Scholar]
  • 29.Bhowmick G.D., Dhar D., Nath D., Ghangrekar M.M., Banerjee R., Das S., Chatterjee J. Coronavirus disease 2019 (COVID-19) outbreak: Some serious consequences with urban and rural water cycle. NPJ Clean Water. 2020;3:32. doi: 10.1038/s41545-020-0079-1. [DOI] [Google Scholar]
  • 30.Achak M., Bakri S.A., Chhiti Y., Alaoui F.E.M., Barka N., Boumya W. SARS-CoV-2 in hospital wastewater during outbreak of COVID-19: A review on detection, survival and disinfection technologies. Sci. Total Environ. 2021;761:143192. doi: 10.1016/j.scitotenv.2020.143192. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 31.Casado-Aranda L.A., Sanchez-Fernandez J., Viedma-del-Jesus M.I. Analysis of the scientific production of the effect of COVID-19 on the environment: A bibliometric study. Environ. Res. 2021;193:110416. doi: 10.1016/j.envres.2020.110416. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 32.Usman M., Ho Y.S. COVID-19 and the emerging research trends in environmental studies: A bibliometric evaluation. Environ. Sci. Pollut. Res. 2021;28:16913–16924. doi: 10.1007/s11356-021-13098-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 33.Sharma G.D., Tiwari A.K., Jain M., Yadav A., Srivastava M. COVID-19 and environmental concerns: A rapid review. Renew. Sust. Energ. Rev. 2021;148:111239. doi: 10.1016/j.rser.2021.111239. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 34.Ji B., Zhao Y., Wei T., Kang P. Water science under the global epidemic of COVID-19: Bibliometric tracking on COVID-19 publication and further research needs. J. Environ. Chem. Eng. 2021;9:105357. doi: 10.1016/j.jece.2021.105357. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 35.Soboji A.O., Zayed T. Impact of sewer overflow on public health: A comprehensive scientometric analysis and systematic review. Environ. Res. 2022;203:111609. doi: 10.1016/j.envres.2021.111609. [DOI] [PubMed] [Google Scholar]
  • 36.Van Eck N.J., Waltman L. Software survey: VOSviewer, a computer program for bibliometric mapping. Scientometrics. 2010;84:523–538. doi: 10.1007/s11192-009-0146-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 37.Van Eck N.J., Waltman L. VOSviewer Manual for Version 1.6.17. CWTS Meaningful Metrics; Universiteit Leiden; Leiden, The Netherlands: 2021. [Google Scholar]
  • 38.Food and Agriculture Organization of the United Nations (FAO) Aquastat, Aquastat Database. 2022. [(accessed on 7 March 2022)]. Available online: https://www.fao.org/aquastat/statistics/popups/itemDefn.html?id=4269.
  • 39.Food and Agriculture Organization of the United Nations (FAO) Aquastat, Aquastat Database. 2022. [(accessed on 7 March 2022)]. Available online: https://www.fao.org/aquastat/statistics/popups/itemDefn.html?id=4188.
  • 40.Food and Agriculture Organization of the United Nations (FAO) Aquastat, Aquastat Database. 2022. [(accessed on 7 March 2022)]. Available online: https://www.fao.org/aquastat/statistics/popups/itemDefn.html?id=4263.
  • 41.Food and Agriculture Organization of the United Nations (FAO) Aquastat, Aquastat Database. 2022. [(accessed on 7 March 2022)]. Available online: https://www.fao.org/aquastat/statistics/popups/itemDefn.html?id=4114.
  • 42.United Nations Development Programme (UNDP) Human Development Report 2020—Human Development Index. Statistical Tables. 2022. [(accessed on 7 March 2022)]. Available online: http://hdr.undp.org/en/content/download-data.
  • 43.The World Bank World Development Indicators–GDP per Capita (Current US$) [(accessed on 7 March 2022)]. Available online: https://data.worldbank.org/indicator/NY.GDP.PCAP.CD.
  • 44.Sangkham S. A review on detection of SARS-CoV-2 RNA in wastewater in light of the current knowledge of treatment process for removal of viral fragments. J. Environ. Manag. 2021;299:113563. doi: 10.1016/j.jenvman.2021.113563. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 45.Torii S., Oishi W., Zhu Y., Thakali O., Malla B., Yu Z., Zhao B., Arakawa C., Kitajima M., Hata A., et al. Comparison of five polyethylene glycol precipitation procedures for the RT-qPCR based recovery of murine hepatitis virus, bacteriophage phi6, and pepper mild mottle virus as a surrogate for SARS-CoV-2 from wastewater. Sci. Total Environ. 2022;807:150722. doi: 10.1016/j.scitotenv.2021.150722. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 46.Ahmed W., Angel N., Edson J., Bibby K., Bivins A., O’Brien J.W., Choi P.M., Kitajima M., Simpson S.L., Li J., et al. First confirmed detection of SARS-CoV-2 in untreated wastewater in Australia: A proof of concept for the wastewater surveillance of COVID-19 in the community. Sci. Total Environ. 2020;728:138764. doi: 10.1016/j.scitotenv.2020.138764. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 47.Wurtzer S., Marechal V., Mouchel J.M., Maday Y., Teyssou R., Richard E., Almayrac J.L., Moulin L. Time course quantitative detection of SARS-CoV-2 in Parisian wastewaters correlates with COVID-19 confirmed cases. MedRxiv. 2020 doi: 10.1101/2020.04.12.20062679. [DOI] [Google Scholar]
  • 48.Kilic T., Weissleder R., Lee H. Molecular and Immunological Diagnostic Tests of COVID-19: Current Status and Challenges. iScience. 2020;23:101406. doi: 10.1016/j.isci.2020.101406. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 49.Heijnen L., Elsinga G., de Graaf M., Molenkamp R., Koopmans M.P.G., Medema G. Droplet digital RT-PCR to detect SARS-CoV-2 signature mutations of variants of concern in wastewater. Sci. Total Environ. 2021;799:149456. doi: 10.1016/j.scitotenv.2021.149456. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 50.Yaniv K., Ozer E., Lewis Y., Kushmaro A. RT-qPCR assays for SARS-CoV-2 variants of concern in wastewater reveals compromised vaccination-induced immunity. Water Res. 2021;207:117808. doi: 10.1016/j.watres.2021.117808. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 51.Chik A.H.S., Glier M.B., Servos M., Mangat C.S., Pang X.L., Qiu Y., D’Aoust P.M., Burnet J.B., Delatolla R., Dorner S., et al. Comparison of approaches to quantify SARS-CoV-2 in wastewater using RT-qPCR: Results and implications from a collaborative inter-laboratory study in Canada. Res. J. Environ. Sci. 2021;107:218–229. doi: 10.1016/j.jes.2021.01.029. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 52.Ahmed W., Bertsch P.M., Bivins A., Bibby K., Farkas K., Gathercole A., Haramoto E., Gyawali P., Korajkic A., McMinn B.R., et al. Comparison of virus concentration methods for the RT-qPCR-based recovery of murine hepatitis virus, a surrogate for SARS-CoV-2 from untreated wastewater. Sci. Total Environ. 2020;39:139960. doi: 10.1016/j.scitotenv.2020.139960. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 53.Flood M.T., D’Souza N., Rose J.B., Aw T.G. Methods Evaluation for Rapid Concentration and Quantification of SARS-CoV-2 in Raw Wastewater Using Droplet Digital and Quantitative RT-PCR. Food Environ. Virol. 2021;13:303–315. doi: 10.1007/s12560-021-09488-8. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 54.Belhaouari D.B., Wurtz N., Grimaldier C., Lacoste A., de Souza G.A.P., Penant G., Hannat S., Baudoin J.P., La Scola B. Microscopic Observation of SARS-Like Particles in RT-qPCR SARS-CoV-2 Positive Sewage Samples. Pathogens. 2021;10:516. doi: 10.3390/pathogens10050516. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 55.O’Brien M., Rundell Z.C., Nemec M.D., Langan L.M., Back J.A., Lugo J.N. A comparison of four commercially available RNA extraction kits for wastewater surveillance of SARS-CoV-2 in a college population. Sci. Total Environ. 2021;801:149595. doi: 10.1016/j.scitotenv.2021.149595. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 56.Hata A., Hara-Yamamura H., Yuno M.Y., Imai S., Honda R. Detection of SARS-CoV-2 in wastewater in Japan during a COVID-19 outbreak. Sci. Total Environ. 2021;758:143578. doi: 10.1016/j.scitotenv.2020.143578. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 57.Navarro A., Gómez L., Sanseverino I., Niegowska M., Roka E., Pedraccini R., Vargha M., Lettieri T. SARS-CoV-2 detection in wastewater using multiplex quantitative PCR. Sci. Total Environ. 2021;797:148890. doi: 10.1016/j.scitotenv.2021.148890. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 58.Mackul’ak T., Gal M., Spalkova V., Feher M., Briestenska K., Mikusova M., Tomcikova K., Tamas M., Skulcova A.B. Wastewater-Based Epidemiology as an Early Warning System for the Spreading of SARS-CoV-2 and Its Mutations in the Population. Int. J. Environ. Res. Public Health. 2021;18:5629. doi: 10.3390/ijerph18115629. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 59.Hui Q., Pan Y., Yang Z. Paper-based devices for rapid diagnostics and testing sewage for early warning of COVID-19 outbreak. Case Stud. Chem. Environ. Eng. 2020;2:100064. doi: 10.1016/j.cscee.2020.100064. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 60.Yang B., Li W., Wang J., Tian Z., Cheng X., Zhang Y., Qiu R., Hou S., Guo H. Estimation of the potential spread risk of COVID-19: Occurrence assessment along the Yangtze, Han, and Fu River basins in Hubei, China. Sci. Total Environ. 2020;746:141353. doi: 10.1016/j.scitotenv.2020.141353. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 61.Bhalla N., Pan Y., Yang Z., Payam A.F. Opportunities and challenges for biosensors and nanoscale analytical tools for pandemics: COVID-19. ACS Nano. 2020;14:7783–7807. doi: 10.1021/acsnano.0c04421. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 62.UI Haque M.F., Bukhari S.S., Ejaz R., Zaman F.U., Sreejith K.R., Rashid N., Umer M., Shahzad N. A novel RdRp-based colorimetric RT-LAMP assay for rapid and sensitive detection of SARS-CoV-2 in clinical and sewage samples from Pakistan. Virus Res. 2021;302:198484. doi: 10.1016/j.virusres.2021.198484. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 63.Nag A., Arora S., Sinha V., Meena E., Sutaria D., Gupta A.B., Medicheria K.M. Monitoring of SARS-CoV-2 Variants by Wastewater-Based Surveillance as a Sustainable and Pragmatic Approach—A Case Study of Jaipur (India) Water. 2022;14:297. doi: 10.3390/w14030297. [DOI] [Google Scholar]
  • 64.Panchal D., Tripathy P., Prakash O., Sharma A., Pal S. SARS-CoV-2: Fate in water environments and sewage surveillance as an early warning system. Water Sci. Technol. 2021;84:1–15. doi: 10.2166/wst.2021.146. [DOI] [PubMed] [Google Scholar]
  • 65.Zahedi A., Monis P., Deere D., Ryan U. Wastewater-based epidemiology—surveillance and early detection of waterborne pathogens with a focus on SARS-CoV-2, Cryptosporidium and Giardia. Parasitol. Res. 2020;120:4167–4188. doi: 10.1007/s00436-020-07023-5. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 66.Bivins A., North D., Ahmad A., Ahmed W., Alm E., Been F., Bhattacharya P., Bijlsma L., Boehm A.B., Brown J., et al. Wastewater-Based Epidemiology: Global Collaborative to Maximize Contributions in the Fight Against COVID-19. Environ. Sci. Technol. 2020;54:7754–7757. doi: 10.1021/acs.est.0c02388. [DOI] [PubMed] [Google Scholar]
  • 67.Randazzo W., Truchado P., Cueva-Ferrando E., Simon P., Allende A., Sanchez G. SARS-CoV-2 RNA in wastewater anticipated COVID-19 occurrence in a low prevalence area. Water Res. 2020;181:115942. doi: 10.1016/j.watres.2020.115942. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 68.Abdeldayem O.M., Dabbish A.M., Habashy M.M., Mostafa M.K., Elhefnawy M., Amin L., Al-Sakkari E.G., Ragab A., Rene E.R. Viral outbreaks detection and surveillance using wastewater-based epidemiology, viral air sampling, and machine learning techniques: A comprehensive review and outlook. Sci. Total Environ. 2022;803:149834. doi: 10.1016/j.scitotenv.2021.149834. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 69.Ahmed W., Bivins A., Simpson S.L., Smith W.J.M., Metcalfe S., McMinn B., Symonds M., Korajkic A. Comparative analysis of rapid concentration methods for the recovery of SARS-CoV-2 and quantification of human enteric viruses and a sewage-associated marker gene in untreated wastewater. Sci. Total Environ. 2021;799:149386. doi: 10.1016/j.scitotenv.2021.149386. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 70.Bivins A., Lott M., Shaffer M., Wu Z., North D., Lipp E.K., Bibby K. Building-level wastewater surveillance using tampon swabs and RT-LAMP for rapid SARS-CoV-2 RNA detection. Environ. Sci. Water Res. Technol. 2022;8:173–183. doi: 10.1039/D1EW00496D. [DOI] [Google Scholar]
  • 71.Gonçalves J., da Silva P.G., Reis L., Nascimento M.S.J., Koritnik T., Paragi M., Mesquita J.R. Surface contamination with SARS-CoV-2: A systematic review. Sci. Total Environ. 2021;798:149231. doi: 10.1016/j.scitotenv.2021.149231. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 72.Majumder A., Gupta A.K., Ghosal P.S., Varma M. A review on hospital wastewater treatment: A special emphasis on occurrence and removal of pharmaceutically active compounds, resistant microorganisms, and SARS-CoV2. J. Environ. Chem. Eng. 2021;9:104812. doi: 10.1016/j.jece.2020.104812. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 73.Khan R., Saxena A., Shukla S., Sekar S., Goel P. Effect of COVID-19 lockdown on the water quality index of River Gomti, India, with potential hazard of faecal-oral transmission. Environ. Sci. Pollut. Res. 2021;28:33021–33029. doi: 10.1007/s11356-021-13096-1. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 74.Zhou N.A., Tharpe C., Meschke J.S., Ferguson C.M. Survey of rapid development of environmental surveillance methods for SARS-CoV-2 detection in wastewater. Sci. Total Environ. 2021;769:144852. doi: 10.1016/j.scitotenv.2020.144852. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 75.Pourakbar M., Abdolahnejad A., Raeghi S., Ghayourdoost F., Yousefi R., Bahnami A. Comprehensive investigation of SARS-CoV-2 fate in wastewater and finding the virus transfer and destruction route through conventional activated sludge and sequencing batch reactor. Sci. Total Environ. 2022;806:151391. doi: 10.1016/j.scitotenv.2021.151391. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 76.Heath A. COVID-19 Water Contamination Concerns Underscore Need to Engage With Consumers. J. Am. Water Work. Assoc. 2020;112:20–25. doi: 10.1002/awwa.1573. [DOI] [Google Scholar]
  • 77.D’Alessio M., Rushing G., Gray T.L. Monitoring water quality through citizen science while teaching STEM undergraduate courses during a global pandemic. Sci. Total Environ. 2021;779:146547. doi: 10.1016/j.scitotenv.2021.146547. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 78.Hallema D.W., Robinne F.N., McNulty S.G. Pandemic spotlight on urban water quality. Ecol. Process. 2020;9:22. doi: 10.1186/s13717-020-00231-y. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 79.Greaves J., Fischer R.J., Shaffer M., Bivins A., Holbrook M.G., Munster V.J., Bibby K. Sodium hypochlorite disinfection of SARS-CoV-2 spiked in water and municipal wastewater. Sci. Total Environ. 2022;807:150766. doi: 10.1016/j.scitotenv.2021.150766. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 80.Buonerba A., Corpuz M.V.A., Ballesteros F., Choo K.H., Hasan S.W., Korshin G.V., Belgiorno V., Barcelo D., Naddeo V. Coronavirus in water media: Analysis, fate, disinfection and epidemiological applications. J. Hazard. Mater. 2021;415:125580. doi: 10.1016/j.jhazmat.2021.125580. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 81.Kostuchenko S.V., Tkachev A.A., Frolikova T.N. UV-technologies for disinfection of water, air and surfaces: Principles and possibilities. Epidemiol. Vaccinal Prev. 2020;19:112–119. doi: 10.31631/2073-3046-2020-19-5-112-119. [DOI] [Google Scholar]
  • 82.Tokatli C., Varol M. Impact of the COVID-19 lockdown period on surface water quality in the Meriç-ErgeCne River Basin. Environ. Res. 2021;197:111051. doi: 10.1016/j.envres.2021.111051. [DOI] [PubMed] [Google Scholar]
  • 83.Huo C., Dar A.A., Nawaz A., Hameed J., Pan B., Wang C. Groundwater contamination with the threat of COVID-19: Insights into CSR theory of Carroll’s pyramid. J. King Saud Univ. Sci. 2021;33:101295. doi: 10.1016/j.jksus.2020.101295. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 84.Qasemi M., Shams M., Sajjadi S.A., Farhang M., Erfanpoor S., Yousef M., Zarei A., Afsharnia M. Cadmium in groundwater consumed in the rural areas of Gonabad and Bajestan, Iran: Occurrence and health risk assessment. Biol. Trace Elem. Res. 2019;192:106–115. doi: 10.1007/s12011-019-1660-7. [DOI] [PubMed] [Google Scholar]
  • 85.Karunanidhi D., Aravinthasamy P., Deepali M., Subramani T., Shankar K. Groundwater Pollution and Human Health Risks in an Industrialized Region of Southern India: Impacts of the COVID-19 Lockdown and the Monsoon Seasonal Cycles. Arch. Environ. Contam. Toxicol. 2021;80:259–276. doi: 10.1007/s00244-020-00797-w. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 86.Vammen K., Guillen S.M. Water Resources of Nicaragua and COVID-19: Between panic and apathy? Braz. J. Biol. 2020;80:690–696. doi: 10.1590/1519-6984.237891. [DOI] [PubMed] [Google Scholar]
  • 87.Mukherjee A., Babu S.S., Ghosh S. Thinking about water and air to attain Sustainable Development Goals during times of COVID-19 Pandemic. J. Earth Syst. Sci. 2020;129:180. doi: 10.1007/s12040-020-01475-0. [DOI] [Google Scholar]
  • 88.Baratta A.F.L., Calcagnini L., Deyoko A., Finucci F., Magaro A., Mariani M. Mitigation of the Water Crisis in Sub-Saharan Africa: Construction of Delocalized Water Collection and Retention Systems. Sustainability. 2021;13:1673. doi: 10.3390/su13041673. [DOI] [Google Scholar]
  • 89.Braga F., Scarpa G.M., Brando V.E., Manfe G., Zaggia L. COVID-19 lockdown measures reveal human impact on water transparency in the Venice Lagoon. Sci. Total Environ. 2020;736:139612. doi: 10.1016/j.scitotenv.2020.139612. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 90.Yan H. Microbial control of river pollution during COVID-19 pandemic based on big data analysis. J. Intell. Fuzzy Syst. 2020;39:8937–8942. doi: 10.3233/JIFS-189291. [DOI] [Google Scholar]
  • 91.Chakraborty B., Roy S., Bera A., Adhikary P.P., Bera B., Sengupta D., Bhunia G.S., Shit P.K. Cleaning the river Damodar (India): Impact of COVID-19 lockdown on water quality and future rejuvenation strategies. Environ. Dev. Sustain. 2021;23:11975–11989. doi: 10.1007/s10668-020-01152-8. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 92.Zhang M., Lian K., Ai L., Kang W., Zhao T. Simultaneous determination of 11 antiseptic ingredients in surface water based on polypyrrole decorated magnetic nanoparticles. RSC Adv. 2020;10:37473. doi: 10.1039/D0RA07064E. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 93.Goswami R., Dey A.K., Dey A. Positive impact on environment due to COVID-19 lockdowns in parts of India: A review. Environ. Eng. Manag. J. 2022;21:559–568. [Google Scholar]
  • 94.Patni K., Jindal M.K. A positive perspective during COVID-19 related to groundwater crisis. Groundw. Sustain. Dev. 2020;11:100420. doi: 10.1016/j.gsd.2020.100420. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 95.Kumar P.S., Yaashikaa P.R. Chapter 1-Introduction. In: Muthu S.S., editor. Water in Textiles and Fashion, Consumption, Footprint, and Life Cycle Assessment. Woodhead Publishing (Elsevier Ltd.); Cambridge, UK: 2019. pp. 1–20. [DOI] [Google Scholar]
  • 96.Fekete A., Sandholz S. Here Comes the Flood, but Not Failure? Lessons to Learn after the Heavy Rain and Pluvial Floods in Germany 2021. Water. 2021;13:3016. doi: 10.3390/w13213016. [DOI] [Google Scholar]
  • 97.Bandala E.R., Kruger B.R., Cesarino I., Leao A.L., Wijesiri B., Goonetilleke A. Impacts of COVID-19 pandemic on the wastewater pathway into surface water: A review. Sci. Total Environ. 2021;774:145586. doi: 10.1016/j.scitotenv.2021.145586. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 98.Neal M.J. COVID-19 and water resources management: Reframing our priorities as a water sector. Water Int. 2020;45:435–440. doi: 10.1080/02508060.2020.1773648. [DOI] [Google Scholar]
  • 99.Stoler J., Jepson W.E., Wutich A. Beyond handwashing: Water insecurity undermines COVID-19 response in developing areas. J. Glob. Health. 2020;10:010355. doi: 10.7189/jogh.10.010355. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 100.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. doi: 10.1016/j.envres.2020.109936. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 101.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. doi: 10.1289/EHP7200. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 102.Hannah D.M., Lynch I., Mao F., Miller J.D., Young S.L., Krause S. Water and sanitation for all in a pandemic. Nat. Sustain. 2020;3:773–775. doi: 10.1038/s41893-020-0593-7. [DOI] [Google Scholar]
  • 103.Adams E.A., Adams Y.J., Koki C. Water, sanitation, and hygiene (WASH) insecurity will exacerbate the toll of COVID-19 on women and girls in low-income countries. Sustain. Sci. Pract. Policy. 2021;17:86–90. doi: 10.1080/15487733.2021.1875682. [DOI] [Google Scholar]
  • 104.García-Ávila F., Avilés-Añazco A., Ordoñez-Jara J., Guanuchi-Quezada C., del Pino L.F., Ramos-Fernández L. Modeling of residual chlorine in a drinking water network in times of pandemic of the SARS-CoV-2 (COVID-19) Sustain. Environ. Res. 2021;31:12. doi: 10.1186/s42834-021-00084-w. [DOI] [Google Scholar]
  • 105.Langone M., Petta L., Cellamare C.M., Ferraris M., Guzzinati R., Mattioli D. SARS-CoV-2 in water services: Presence and impacts. Environ. Pollut. 2020;268:115806. doi: 10.1016/j.envpol.2020.115806. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 106.Siddiqui R., Khamis M., Ibrahim T., Khan N.A. SARS-CoV-2: The increasing importance of water filtration against highly pathogenic microbes. ACS Chem. Neurosci. 2020;11:2482–2484. doi: 10.1021/acschemneuro.0c00468. [DOI] [PubMed] [Google Scholar]
  • 107.Tleuken A., Tokazhanov G., Serikbay A.B., Zhalgasbayev K., Guney M., Turkyilmaz A., Karaca F. Household water and energy consumption changes during COVID-19 pandemic lockdowns: Cases of Kazakhstani Cities of Almaty, Shymkent, and Atyrau. Buildings. 2021;11:663. doi: 10.3390/buildings11120663. [DOI] [Google Scholar]
  • 108.Kazak J.K., Szewranski S., Pilawka T., Tokarczyk-Dorociak K., Janiak K., Swiadwe M. Changes in water demand patterns in a European city due to restrictions caused by the COVID-19 pandemic. Desalin. Water Treat. 2021;222:1–15. doi: 10.5004/dwt.2021.27242. [DOI] [Google Scholar]
  • 109.Di Mauro A., Santonastaso G.F., Venticinque S., Di Nardo A. Impact of COVID-19 emergency on residential water end-use consumption measured with a high-resolution IoT system. AQUA Water Infrastruct. Ecosyst. Soc. 2021;70:1248–1256. doi: 10.2166/aqua.2021.088. [DOI] [Google Scholar]
  • 110.Balacco G., Totaro V., Iacobellis V., Manni A., Spagnoletta M., Piccini A.F. Influence of COVID-19 spread on water drinking demand: The case of Puglia Region (Southern Italy) Sustainability. 2020;12:5919. doi: 10.3390/su12155919. [DOI] [Google Scholar]
  • 111.Changklom J., Surasaranwong T., Jowwongsan P., Lipiwattanakarn S., Pornprommin A. Impact of COVID-19 on monthly water consumption on a tropical tourism island: Case study of Phuket (Thailand) Water Supply. 2021;22:3419–3430. doi: 10.2166/ws.2021.396. [DOI] [Google Scholar]
  • 112.Sowby R.B., Lunstad N.T. Considerations for Studying the Impacts of COVID-19 and Other Complex Hazards on Drinking Water Systems. J. Infrastruct. Syst. 2021;27:02521002-1–02521002-5. doi: 10.1061/(ASCE)IS.1943-555X.0000658. [DOI] [Google Scholar]
  • 113.Deem S. Preparing for COVID-19’s effect on Legionella and building water systems. J. Am. Water Work. Assoc. 2020;112:60–62. doi: 10.1002/awwa.1578. [DOI] [Google Scholar]
  • 114.Liang J., Swanson C.S., Wang L., He Q. Impact of building closures during the COVID-19 pandemic on Legionella infection risks. Am. J. Infect. Control. 2021;49:1564–1566. doi: 10.1016/j.ajic.2021.09.008. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 115.Turetgen I. Legionella surveillance in stagnant water systems during COVID-19 lockdown in Istanbul. Malays. J. Microbiol. 2021;17:720–724. doi: 10.21161/mjm.211187. [DOI] [Google Scholar]
  • 116.Proctor C., Rhoads W., Keane T., Salehi M., Hamilton K., Pieper K., Cwiertny D., Prevost M., Whelton A. Considerations for large building water quality after extended stagnation. AWWA Water Sci. 2020;2:e1186. doi: 10.1002/aws2.1186. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 117.Asadi-Ghalhari M., Aali R. COVID-19: Reopening public spaces and secondary health risk potential via stagnant water in indoor pipe networks. Indoor Built Environ. 2020;29:1184–1185. doi: 10.1177/1420326X20943257. [DOI] [Google Scholar]
  • 118.Ekanayake A., Rajapaksha A.U., Hewawasam C., Anand U., Bontempi E., Kurwadkar S., Biswas J.K., Vithanage M. Environmental Challenges of COVID-19 pandemic: Resilience and sustainability—A review. Environ. Res. 2023;216:114496. doi: 10.1016/j.envres.2022.114496. [DOI] [PMC free article] [PubMed] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Availability Statement

Not applicable.


Articles from International Journal of Environmental Research and Public Health are provided here courtesy of Multidisciplinary Digital Publishing Institute (MDPI)

RESOURCES