Management of Conventional and Non-Conventional Water Sources: A Systematic Literature Review
Abstract
1. Introduction
2. Materials and Methods
2.1. Selection of Search Keywords
2.2. Selection of Search Parameters
2.3. Building and Tailoring the Search String
2.4. Conducting the Initial Search and Eligibility Assessment
- Studies on flood risk management unrelated to WS management;
- Studies on water demand forecasting that are not linked to specific WSs;
- Studies of societal inequality in access to water;
- Studies on societal behavior regarding water usage;
- Studies on renewable energy unrelated to water management;
- Studies of pricing in water markets;
- Studies of AI-powered water quality index prediction;
- Studies related to climate change impacts on water resources;
- Studies on specific ICT technologies, including data collection, data Storage, data analysis, data protection, and cybersecurity in water systems.
2.5. Evaluation of Results
3. Results
3.1. PRISMA Flow Diagram
3.2. Database Split
3.3. Temporal Trends
3.4. Research Fields and Geographic Coverage
3.5. Water Sources Categorization
4. Discussion
5. Conclusions
Author Contributions
Funding
Data Availability Statement
Conflicts of Interest
Abbreviations
HWSM | Hybrid Water Systems Management |
PRISMA | Preferred Reporting Items for Systematic Reviews and Meta-Analyses |
UN | United Nations |
WSs | Water Sources |
VOSviewer | Visualization of Similarities Viewer |
Appendix A
Database Name | Suggested Query Strings for Search |
---|---|
Scopus | TITLE-ABS-KEY (“Water Source” OR “Conventional water” OR “Non-conventional water” OR “Water Supply System” OR “Water Resource System”) AND (“Surface water” OR Groundwater OR “Brackish water” OR Effluent OR Greywater OR “Reclaimed wastewater” OR “Harvested rainwater” OR “Harvested stormwater” OR “Atmospheric Water” OR “Desalinated water” OR “Urban runoff”) AND NOT (Health OR Biodiversity OR Climate OR Educat OR Culture OR Energy OR Hydrodynamic OR Ecology) AND DOCTYPE (ar OR re) AND (PUBYEAR > 1999 AND PUBYEAR < 2024) AND (LIMITTO (LANGUAGE, ”English”)) |
Web of Science Core Collections | # 1 (TS = (“Water Source *” OR “Conventional water *” OR “Non-conventional water *” OR “Water Supply System *” OR “Water Resource System *”)) AND LANGUAGE: (English) AND DOCUMENT TYPES: (Article) # 2 (TS = (“Surface water *” OR Groundwater * OR “Brackish water *” OR Effluent OR Greywater OR “Reclaimed wastewater” OR “Harvested rainwater” OR “Harvested stormwater” OR “Atmospheric Water *” OR “Desalinated water *” OR “Urban runoff *”)) AND LANGUAGE: (English) AND DOCUMENT TYPES: (Article) # 3 # 2 AND # 1 # 4 (TS = (Health * OR Biodiversity OR Design * OR Climate OR Educat * OR Culture * OR Energy * OR Hydrodynamic * OR Ecology)) AND LANGUAGE: (English) AND DOCUMENT TYPES: (Article) # 5 (# 3 NOT # 4) AND LANGUAGE: (English) AND DOCUMENT TYPES: (Article) |
ScienceDirect | Find articles with these terms: (“Water Source” OR “Conventional water” OR “Non-conventional water” OR “Water Supply System” OR “Water Resource System”) |
Year: 1999–2024 | |
Title, abstract, keywords: NOT (Health OR Biodiversity OR Climate OR Educat OR Culture OR Energy OR Hydrodynamic OR Ecology) | |
Title: (“Surface water” OR Groundwater OR “Brackish water” OR Effluent OR Greywater OR “Reclaimed wastewater” OR “Harvested rainwater” OR “Harvested stormwater” OR “Atmospheric Water” OR “Desalinated water” OR “Urban runoff”) | |
Article types: Review articles, Research articles |
Appendix B
№ | Publication | Topic | Location | Water Source | Main Results |
---|---|---|---|---|---|
1 | Abu Qdais & Batayneh [63] | The role of desalination in bridging the water gap in Jordan | Hashemite Kingdom of Jordan, 2000–2020 | Groundwater; surface water; desalinated water | This study assesses Jordan’s water resources, future demand, and the demand-supply gap under two scenarios, exploring desalination as a potential solution. While seawater desalination is currently not cost-effective for domestic use, desalination of brackish water using reverse osmosis is the most practical short-term option. |
2 | Talaat et al. [64] | The potential role of brackish water desalination within the Egyptian water supply matrix | Egypt, 2001 | Groundwater and desalinated water | The study examines challenges in Egypt’s brackish water desalination and presents a case study on reverse osmosis to assess its feasibility as compared to other water supply options. The findings highlight reverse osmosis desalination as a cost-effective solution, supporting the need for large-scale implementation. |
3 | Voivontas et al. [65] | Water supply modeling towards sustainable environmental management in small islands | Paros, Greece, 2002 | Groundwater; surface water; desalinated water and water hauling by ships/fresh water | An optimization model was developed to minimize the Net Present Value of projected water supply costs for the period 2002–2030. The results illustrate that conventional water sources, supplemented by flexible desalination systems to address water consumption peaks, offer the most effective solution for the island of Paros. |
4 | Al-Ruwaih & Almedeij [66] | The future sustainability of water supply in Kuwait | Kuwait, 2010 | Groundwater; distilled water; desalinated seawater | The paper evaluates Kuwait’s water resources to develop an integrated management plan with a focus on sustainability. Given the constraints on conventional and non-conventional water sources amid a growing population, wastewater recycling for irrigation, industry, and other non-potable uses is essential. |
5 | Al-Katheeri [67] | Towards the establishment of water management in Abu Dhabi Emirate | Abu Dhabi, United Arab Emirates, 2006 | Brackish water; groundwater; fresh water; treated wastewater; desalinated water | The need for water management is critical. Adequate storage capacity addresses some of the challenges associated with freshwater supply. The Emirate of Abu Dhabi requires long-term storage capacity equivalent to at least one year’s freshwater demand. One method of increasing this capacity is artificial recharge using surplus desalinated water produced from treated wastewater. |
6 | Blute et al. [68] | Integration of desalinated seawater into a distribution system. | Carlsbad, California, USA, 2007 | Desalinated seawater and surface water | The findings support the sustainable integration of desalinated water alongside conventional sources while ensuring long-term infrastructure reliability. |
7 | Gikas & Angelakis [69] | Water resources management in Crete and in the Aegean Islands, with emphasis on the utilization of non-conventional water sources | Crete and the Aegean Islands, 2007 | Groundwater, surface water, desalinated seawater; reclaimed wastewater and brackish water; rainwater catchment | The study highlights water scarcity in Crete and the Aegean Islands, where limited resources and geographical constraints hinder integrated management. It highlights the potential of non-conventional sources like desalination and wastewater reuse to address shortages. Sustainable water management strategies are crucial for long-term resilience in these regions. |
8 | Lahav et al. [70] | Chemical stability of inline blends of desalinated, surface and ground waters | Israel, 2008 | Groundwater; surface water; desalinated water | Simulation results for an Israeli water distribution model demonstrate that desalinated water with low alkalinity causes chemical instability upon mixing, while increasing alkalinity ensures constant calcium carbonate precipitation potential values. |
9 | Housh et al. [71] | Box-Constrained Optimization Methodology and Its Application for a Water Supply System Model | Israel, 2011 | Groundwater and desalinated water | The study presents the search method for box optimization, a heuristic optimization method that outperforms or matches genetic algorithms in benchmark tests and is found to be effective for solving nonlinear water supply system management problems. |
10 | Housh et al. [72] | Limited multi-stage stochastic programming for managing water supply systems | Israel, 2012 | Groundwater and desalinated water | The study proposes a limited multi-stage stochastic programming method that simplifies complex water supply optimization under uncertainty by clustering similar decisions, enabling efficient and scalable decisions. |
11 | Nápoles-Rivera et al. [73] | Sustainable water management for macroscopic systems | Morelia, Mexico, 2012 | Potable water *; rainwater and reclaimed water | The paper presents a mathematical model for sustainable water management, optimizing the distribution and storage of conventional and non-conventional water sources. The model demonstrates that incorporating rainwater and reclaimed water can reduce freshwater consumption and waste while remaining economically viable. The approach highlights the potential of non-conventional water sources in enhancing sustainability. |
12 | Al-Juaidi et al. [74] | Hydrologic-Economic Model for Sustainable Water Resources Management in a Coastal Aquifer. | Gaza Strip, 2013 | Groundwater; treated wastewater and desalinated seawater | The study presents an optimization model for Gaza’s water system by balancing groundwater use, desalination, and wastewater reuse. The results show that water reallocation and a 2% annual reduction in agriculture can mitigate groundwater depletion while improving economic viability. Integrating desalination and wastewater reuse increases sustainability, reduces costs, and supports long-term water security. |
13 | Asefa et al. [75] | A tale of integrated regional water supply planning: Meshing socio-economic, policy, governance, and sustainability desires together | Florida, USA, 2013 | Groundwater; surface water, and desalinated seawater | Tampa Bay Water reduced groundwater use by over 50% in under a decade, diversifying supply with groundwater, surface water, and desalinated seawater. Their advanced forecasting and decision-making tools improved lake and wetland levels while ensuring sustainable water availability for 23 million customers. |
14 | dos Santos & Benetti [76] | Application of the urban water use model for urban water use management purposes | Seara city, Santa Catarina State, Brazil, 2013 | Potable water *; greywater; wastewater | This study applies the Urban Water Use model to identify the most effective water management strategies for Seara, Brazil. By evaluating various alternatives, the model highlighted water demand management and decentralized sanitation as the most impactful measures for improving urban water efficiency and sustainability. |
15 | Behzadian & Kapelan [77] | Advantages of integrated and sustainability-based assessment for metabolism based strategic planning of urban water systems | City of northern Europe, 2010–2014 | Potable water *; stormwater; wastewater, and water recycling | This paper compares traditional water supply planning with an integrated urban water system approach, including potable water, stormwater, wastewater, and recycling. Using the WaterMet model, it finds that strategies like rainwater harvesting and greywater recycling are more effective in integrated systems, emphasizing the need for both conventional and sustainability criteria in long-term urban water systems planning. |
16 | Ward & Becker [78] | Cost of water for peace and the environment in Israel: An integrated approach | Israel, 2012 | Potable water *; Marginal saline water and desalinated sea water | The optimization model shows that integrated water resources management and desalination can ensure cost-effective water distribution in Israel, supporting both peace efforts and environmental goals. |
17 | Al-Zahrani et al. [79] | Multi-objective optimization model for water resource management | Riyadh city, Saudi Arabia, 2015 | Groundwater; desalinated water and treated wastewater | A multi-objective goal programming model was developed for water distribution from multiple sources (groundwater, desalinated water, and treated wastewater) to multiple users (domestic, agricultural, and industrial sectors). The results show that desalinated water supply and treated wastewater reuse need to be increased to meet projected volumes during 2015–2050. |
18 | Luckmann et al. [80] | Modeling economy-wide linkages of wastewater use | Israel, 2004 | Potable water *; reclaimed wastewater and brackish water | A Computable General Equilibrium model reveals that the decline in potable water increases the demand for reclaimed wastewater, supports pricing strategies, and shows limited substitution when recycling is already high. |
19 | Zavala et al. [81] | Potential of Rainwater Harvesting and Greywater Reuse for Water Consumption Reduction and Wastewater Minimization | Monterrey, Mexico, 2015 | Potable water *; rainwater and greywater | The results showed that water consumption could be reduced by 48% and wastewater generation could be minimized by 59%. Integrating rainwater harvesting with greywater treatment and reuse would not only reduce potable water consumption and wastewater treatment needs but would also contribute to significant savings for water users and water and wastewater system operators. |
20 | George et al. [82] | Effects of two different water sources used for irrigation on the soil geochemical properties | Kuala Lumpur, Malaysia, 2016 | Treated wastewater and surface water | This study examined the impact of treated wastewater and lake water irrigation on soil geochemistry and Lohan guava quality. Treated wastewater met irrigation standards, while lake water fell short. Water sources significantly affected soil properties and fruit quality, with irrigation quality positively influencing fruit attributes and consumer acceptance. |
21 | Nel et al. [83] | Supplementary household water sources to augment potable municipal supply in South Africa | Western Cape, Republic of South Africa, 2016 | Potable water *; greywater, rainwater and stormwater | This study examines groundwater abstraction, rainwater harvesting, and greywater reuse as household water sources in South Africa. The proposed end-use model estimates a 55–69% reduction in municipal water demand when these sources are maximally used. While they help alleviate supply pressures, their integration complicates water planning and management, requiring further research. |
22 | Porse et al. [84] | Systems Analysis and Optimization of Local Water Supplies in Los Angeles | Los Angeles, USA, 2016 | Potable water *; wastewater, and stormwater | The network flow model was developed to explore management trade-offs between engineering, social, and environmental systems. With aggressive regional demand, increased stormwater capture (300%), and prioritized reuse of water from existing facilities, imported water supplies can be reduced by 30% while maintaining landscapes, economic productivity, and groundwater resources. Further reductions in imports (40–50%) are possible through additional reuse, recharge, conservation, and access to groundwater. |
23 | Reznik et al. [27] | Agricultural reuse of treated wastewater in Israel | Israel, 2016 | Groundwater; desalinated water; treated wastewater and brackish water | The study identified that agricultural reuse of treated wastewater is an optimal water management strategy under water conditions, mainly as a cost-effective way to transfer freshwater from the agriculture to the urban sector. |
24 | Ao et al. [85] | Replenishment of landscape water with reclaimed water | China, 2013–2015 | Surface water; potable/urban water *; reclaimed water | With urban water shortages, reclaimed water (RW) is increasingly used for landscape water replenishment. A mathematical model analyzed its impact on water quality in a northwest Chinese city. While RW’s higher nutrients may boost algae growth, its lower suspended solids improve water clarity. Simulations using MIKE 3 showed that with optimal RW use, inflow needs decreased. A water supply scheme of RW replenishment for the surface water body (with water transparency as the control indicator) was proposed. |
25 | Podda et al. [86] | Blending between desalinated water and other sources | Italy, 2017 | Groundwater and desalinated water | A comprehensive blending tool, integrated with a hydrogeological dynamic verification tool, was developed by Lotti Ingegneria, Italy. Based on a database of groundwater and blending points (desalinated water and groundwater), the tool monitors and controls desalinated water blending in real time to ensure optimal water quality. |
26 | Tsur & Zemel [87] | Water policy guidelines: A comprehensive approach | Israel, 2017 | Groundwater; surface water; desalinated water and recycled water | The study models the optimal allocation of water and investment between sources and sectors, showing that infrastructure must quickly reach efficient (turnpike) paths and then stabilize, with implications for pricing, processing, and desalination times. |
27 | Aparicio et al. [88] | Agricultural irrigation of vine crops from desalinated and groundwater | Siġġiewi, Malta, 2018 | Groundwater and desalinated water | Two irrigation scenarios were considered: groundwater irrigation or “do nothing” versus “use of non-conventional water” by blending water from a small desalination plant and groundwater. Blending desalinated water with groundwater improves water availability, quality, and farm profitability. The study finds desalination to be the best non-conventional water option, with a small reverse osmosis plant (120 m3/day) supporting irrigation needs profitably from a minimum area of 1 ha. |
28 | Porse & Pincetl [89] | Effects of Stormwater Capture and Use on Urban Streamflows | Los Angeles, USA, 2017 | Groundwater, surface water; recycled water, and stormwater | Using a simulation and optimization model for regional urban water management, the potential impact of increased stormwater was captured and infiltration on urban flow was analyzed. Results show that for many watersheds in Los Angeles, further increases in stormwater capture and use would significantly reduce urban flow. The results illustrate the potential tradeoffs in water supply, river flows, and aquatic habitat that must be considered when attempting to increase local water use by increasing stormwater. |
29 | Qi et al. [90] | Making Rainwater Harvesting a Key Solution for Water Management | East African Rift System, East Africa, 2018 | Groundwater; rainwater; stormwater | This paper presents an expansion of the original Kilimanjaro Concept by incorporating Chinese experience to demonstrate the universal applicability of KC for water management. Ongoing efforts to implement the Kilimanjaro Concept in the East African Rift Valley demonstrate that rainwater harvesting is a potential universal solution to meet ever-increasing water needs, while also assisting in groundwater recharge, reducing flooding and soil erosion. |
30 | Silva et al. [91] | Proposal of integrated urban waters management as a strategy to promote water security | Fortaleza, Brazil, 2018 | Surface water; groundwater; rainwater; desalinated water | The study proposes the use of the integrated urban water management model. The model is based on the management of water supply and water demand. The proposed model diversifies supply with surface water, groundwater, rainwater, and desalination, while demand management includes water-saving fixtures and financial incentives. This approach strengthens urban water security through a more resilient supply matrix. |
31 | Al-Juaidi & Attiah [92] | Evaluation of desalination and groundwater supply sources for future water resources management | Riyadh city, Saudi Arabia, 2017–2019 | Groundwater and desalinated water | This paper examines the effectiveness of desalination and groundwater supply on water demand based on the Water Evaluation and Planning model. Without intervention, unmet demand could reach 1076 MCM by 2030. Strategies like water conservation, leak reduction, and recycled water reuse lower future deficits, ensuring a more sustainable supply. |
32 | Finkelshtain et al. [93] | Substitutability of Freshwater and Non-Freshwater Sources in Irrigation | Israel, 2019 | Potable water *; treated wastewater | The simulations indicate that the Israeli quota-exchange policy has increased both agricultural production value and farming profits. |
33 | Slater et al. [94] | Large-Scale Desalination and the External Impact on Irrigation-Water Salinity | Israel, 2015 | Surface water; groundwater; treated wastewater; desalinated water | Using a dynamic hydroeconomic model, the study shows that accounting for irrigation water salinity justifies large-scale desalination in Israel, preventing a 29% drop in farm profits and avoiding significant deadweight losses per hectare. |
34 | Zhang et al. [95] | Numerical Simulation of Multi-Water-Source Artificial Recharge of Aquifer | Mi-Huai-Shun area, China, 2007–2016 | Surface water; groundwater; reclaimed water | Artificial recharge helps to solve the problem of water scarcity and groundwater depletion. Numerical simulations in the Mi-Huai-Shun area evaluated a multi-source groundwater recharge reservoir using reclaimed water, treated wetland water, and SNWTP (South–North Water Transfer Project) water. The results showed that groundwater levels recovered, and reserves increased, but chloride levels increased with reclaimed and wetland water. Chloride concentrations in SNWTP water are diluted, highlighting its role in improving water quality. |
35 | Housh & Aharon [96] | Info-Gap Models for Optimal Multi-Year Management of Regional Water Resources Systems under Uncertainty | Israel, 2020 | Surface water; groundwater; desalinated water | The study develops an Info-Gap Decision Theory-based model for managing water supply systems under deep uncertainty, demonstrating its use on the Sea of Galilee system to support robust, long-term planning amid climate change and non-stationary conditions. |
36 | Gómez-Monsalve et al. [97] | Environmental performance of a hybrid rainwater harvesting and greywater reuse system | Bucaramanga, Colombia, 2021 | Potable water *; greywater and rainwater | This study compares the environmental performance of a hybrid rainwater harvesting and greywater reuse system with a conventional centralized water system. Using Life Cycle Assessment (LCA) with GaBi software, the study found that the hybrid system saves about 131 m3/year of potable water, reducing total consumption by 42.5% and wastewater treatment plant flows by 20%. Furthermore, the hybrid system showed lower environmental impacts. |
37 | Moradikian et al. [98] | A distributed constraint multi-agent model for water and reclaimed wastewater allocation in urban areas | Tehran, Iran, 2021 | Surface; groundwater; reclaimed wastewater | This study develops a Distributed Constraint Optimization (DCOP)-based model for allocating urban water and reclaimed wastewater, balancing stakeholders’ conflicting interests. A modified ADOPT algorithm (MADOPT) introduces an agent for monitoring and conservation, incorporating social dynamics. Applied to urban water allocation, MADOPT proves effective for large-scale multi-agent systems, demonstrating how agents’ social behaviors influence water use policies. |
38 | Ribeiro et al. [99] | Diversification of urban water supply: an assessment of social costs and water production costs | Fortaleza, Brazil, 2019 | Groundwater; surface water; desalinated water; treated wastewater; greywater; rainwater | This study assesses the economic feasibility of integrating new water sources by analyzing production and social costs. Desalination (USD 0.28/m3) and industrial reuse (USD 0.57/m3) are cost-effective, while cisterns and greywater reuse are more expensive. Well water is the cheapest (USD 0.08/m3). Desalination and industrial reuse are reliable, but tariffs do not reflect their full social costs. |
39 | Zafeirakou et al. [100] | Water resources management in the framework of the circular economy for touristic areas in the Mediterranean | Sifnos Island, Greece,2021 | Groundwater; natural springs; rainwater, and desalinated water | The study compares Sifnos’s water management model to Singapore’s, as both use rainwater and desalination. Sifnos relies on groundwater, springs, cisterns, reservoirs, and desalination. The study aims to improve sustainability over 20 years by incorporating wastewater reuse for irrigation, firefighting, and potential potable use. The findings offer a framework for water autonomy that could be applied to other islands and coastal tourism areas. |
40 | Gilboa et al. [101] | Assessing water use and reuse options-a holistic analysis of a Model City, coupling dynamic system modeling with Life Cycle Assessment | Future Model City under typical Israeli conditions, 2022 | Potable water *, rainwater, greywater, and treated wastewater | A dynamic model was developed to assess water reuse in an urban system, integrating Life Cycle Assessment and Life Cycle Costing. The model compares six scenarios using different water sources (potable, rainwater, greywater, and treated wastewater) for a future city under Israeli conditions. The results show that using treated greywater or treated wastewater for non-potable uses is the most economical. The business-as-usual scenario, relying solely on potable water, has the highest environmental impacts. |
41 | Hendrickson et al. [102] | Optimizing desalination for regional water systems | Israel, 2022 | Surface water; groundwater; desalinated water | The study applies two-stage optimization and multi-criteria decision analysis to the Israeli water system, showing how desalination can be effectively integrated under uncertainty by balancing early production decisions with flexible supply allocation and stakeholder benefits. |
42 | Housh [103] | Optimizing bilinear multi-source water supply systems using mixed-integer linear programming approximations | Israel, 2020 | Surface water; groundwater; desalinated water | The study proposes MILP-based formulas for optimizing multi-source water supply management, demonstrating that they effectively solve the complex model of the Israeli water supply system and allow for optimal use of both conventional and non-conventional water sources. |
43 | Abbasmiri et al. [104] | Quantitative and qualitative management of water resources with the use of treated wastewater | Tehran, Iran, 2023 | Groundwater and treated wastewater | An optimization model for the joint use of treated wastewater and groundwater was used to allocate traditional and non-traditional water resources. The model results showed that the volume of water withdrawal for irrigation would be reduced if the Rei treatment plant and irrigation and drainage network were built. The results show that under existing conditions, the net benefit of the system would decrease in search of an optimal economic and environmental state. |
44 | Shi et al. [105] | Optimal Allocation of Water Resources in Ordos City Based on the General Water Allocation and Simulation Model | Ordos City, the Inner Mongolia Autonomous Region, China, 2010–2021 | Surface water; groundwater; dredging water; reclaimed water; and rainwater | This study develops a multi-objective model to optimize water resource allocation for Ordos City. The model forecasts water shortages in specific districts by 2025 and 2030, especially during agricultural use, but shows a shift from groundwater to surface and unconventional water sources, improving efficiency and reducing overexploitation. As a result, the regional water supply structure was optimized, with groundwater decreasing from 49.08% in 2025 to 43.35% in 2030, while surface water and unconventional water proportions increased. |
Appendix C
Section and Topic | Item # | Checklist Item | Location Where Item Is Reported |
---|---|---|---|
TITLE | |||
Title | 1 | Identify the report as a systematic review. | See p. 1 |
ABSTRACT | |||
Abstract | 2 | See the PRISMA 2020 for Abstracts checklist. | See p. 1 |
INTRODUCTION | |||
Rationale | 3 | Describe the rationale for the review in the context of existing knowledge. | See pp. 1–4 |
Objectives | 4 | Provide an explicit statement of the objective(s) or question(s) addressed in the review. | See p. 3 |
METHODS | |||
Eligibility criteria | 5 | Specify the inclusion and exclusion criteria for the review and how the studies were grouped for the syntheses. | See p. 5, 2nd paragraph |
Information sources | 6 | Specify all databases, registers, websites, organizations, reference lists and other sources searched or consulted to identify studies. Specify the date when each source was last searched or consulted. | See p. 6, 1st paragraph |
Search strategy | 7 | Present the full search strategies for all databases, registers, and websites, including any filters and limits used. | See pp. 5–7 |
Selection process | 8 | Specify the methods used to decide whether a study met the review inclusion criteria, including how many reviewers screened each record and each report retrieved, whether they worked independently and, if applicable, details of automation tools used in the process. | See p. 6, 4th and 5th paragraphs |
Data collection process | 9 | Specify the methods used to collect data from reports, including how many reviewers collected data from each report, whether they worked independently, any processes to obtain or confirming data from study investigators, and, if applicable, details of automation tools used in the process. | See p. 7, 2nd paragraphs |
Data items | 10a | List and define all outcomes for which data were sought. Specify whether all results that were compatible with each outcome domain in each study were sought (e.g., for all measures, time points, analyses), and if not, the methods used to decide which results to collect. | Reported in Figure 2 |
10b | List and define all other variables for which data were sought (e.g., participant and intervention characteristics, funding sources). Describe any assumptions made about any missing or unclear information. | - | |
Study risk of bias assessment | 11 | Specify the methods used to assess risk of bias in included studies, including details of the tool(s) used, how many reviewers assessed each study and whether they worked independently, and if applicable, details of the automation tools used in the process. | See p. 4, 1st paragraphs |
Effect measures | 12 | Specify for each outcome the effect measure(s) (e.g., risk ratio, mean difference) used in the synthesis or presentation of results. | - |
Synthesis methods | 13a | Describe the processes used to decide which studies were eligible for each synthesis (e.g., tabulating the study intervention characteristics and comparing against the planned groups for each synthesis (item # 5)). | See p. 6, 4th and 5th paragraphs |
13b | Describe any methods required to prepare the data for presentation or synthesis, such as handling missing summary statistics, or data conversions. | - | |
13c | Describe any methods used to tabulate or visually display the results of individual studies and syntheses. | See p. 7, 2nd paragraph | |
13d | Describe any methods used to synthesize the results and provide a rationale for the choice(s). If a meta-analysis was performed, describe the model(s), method(s) to identify the presence and extent of statistical heterogeneity, and software package(s) used. | - | |
13e | Describe any methods used to explore possible causes of heterogeneity among study results (e.g., subgroup analysis, meta-regression). | - | |
13f | Describe any sensitivity analyzes conducted to assess robustness of the synthesized results. | - | |
Reporting bias assessment | 14 | Describe any methods used to assess the risk of bias due to missing results in a synthesis (arising from reporting biases). | - |
Certainty assessment | 15 | Describe any methods used to assess the certainty (or confidence) in the body of evidence for an outcome. | See p. 4, 1st paragraphs |
RESULTS | |||
Study selection | 16a | Describe the results of the search and selection process, from the number of records identified in the search to the number of studies included in the review, ideally using a flow chart. | Reported in Figure 3 |
16b | Cite studies that might appear to meet the inclusion criteria, but were excluded, and explain why they were excluded. | - | |
Study characteristics | 17 | Cite each included study and present its characteristics. | Reported in Appendix B |
Risk of bias in studies | 18 | Present evaluations of risk of bias for each included study. | See p. 5, 1st and 2nd paragraphs |
Results of individual studies | 19 | For all outcomes, present, for each study: (a) summary statistics for each group (where appropriate), and (b) an effect estimates and its precision (e.g., confidence/credible interval), ideally using structured tables or plots. | See pp. 7–13 |
Results of syntheses | 20a | For each synthesis, briefly summarize the characteristics and risk of bias among contributing studies. | - |
20b | Present results of all statistical syntheses conducted. If a meta-analysis was done, present for each the summary estimate and its precision (e.g., confidence/credible interval) and measures of statistical heterogeneity. If comparing groups, describe the direction of the effect. | - | |
20c | Present results of all investigations of possible causes of heterogeneity among study results. | - | |
20d | Present results of all sensitivity analyses conducted to assess the robustness of the synthesized results. | - | |
Reporting biases | 21 | Present assessments of risk of bias due to missing results (arising from reporting biases) for each synthesis assessed. | See p. 5, 2nd paragraph |
Certainty of evidence | 22 | Present assessments of certainty (or confidence) in the body of evidence for each outcome assessed. | - |
DISCUSSION | |||
Discussion | 23a | Provide a general interpretation of the results in the context of other evidence. | See pp. 13–16 |
23b | Discuss any limitations of the evidence included in the review. | See p. 16, 6th paragraph | |
23c | Discuss any limitations of the review processes used. | See p. 16, 6th paragraph | |
23d | Discuss implications of the results for practice, policy, and future research. | See p. 16, 6th paragraph | |
OTHER INFORMATION | |||
Registration and protocol | 24a | Provide registration information for the review, including register name and registration number, or state that the review was not registered. | - |
24b | Indicate where the review protocol can be accessed, or state that a protocol was not prepared. | - | |
24c | Describe and explain any amendments to information provided at registration or in the protocol. | - | |
Support | 25 | Describe sources of financial or non-financial support for the review, and the role of the funders or sponsors in the review. | See p. 17 |
Competing interests | 26 | Declare any competing interests of review authors. | See p. 17 |
Availability of data, code and other materials | 27 | Report which of the following are publicly available and where they can be found: template data collection forms; data extracted from included studies; data used for all analyses; analytic code; any other materials used in the review. | See p. 17 |
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№ | Water Type | Water Source | Country |
---|---|---|---|
1 | Conventional | Groundwater | Brazil, China, Crete, East Africa, Egypt, Greece, Iran, Israel, Italy, Jordan, Kuwait, Malta, Saudi Arabia, UAE, USA |
2 | Surface Water | Brazil, China, Crete, Greece, Iran, Israel, Jordan, Malaysia, USA | |
3 | Fresh/Potable Water | Brazil, China, Colombia, Greece, Israel, Mexico, Northern Europe, Republic of South Africa, UAE, USA | |
4 | Non-Conventional | Desalinated Seawater | Brazil, Crete, Egypt, Greece, Israel, Italy, Jordan, Kuwait, Malta, Saudi Arabia, UAE, USA |
5 | Brackish water | Crete, Israel, UAE | |
6 | Reclaimed/Treated Wastewater | Brazil, China, Crete, Gaza Strip, Iran, Israel, Malaysia, Mexico, northern Europe, Saudi Arabia, UAE, USA | |
7 | Rainwater | Brazil, China, Colombia, East Africa, Greece, Israel, Mexico, Republic of South Africa | |
8 | Greywater | Brazil, Colombia, Israel, Mexico, Republic of South Africa | |
9 | Stormwater | East Africa, Northern Europe, Republic of South Africa, USA | |
10 | Dredging Water | China | |
11 | Distilled Water | Kuwait |
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Dashkevych, O.; Housh, M. Management of Conventional and Non-Conventional Water Sources: A Systematic Literature Review. Water 2025, 17, 3006. https://doi.org/10.3390/w17203006
Dashkevych O, Housh M. Management of Conventional and Non-Conventional Water Sources: A Systematic Literature Review. Water. 2025; 17(20):3006. https://doi.org/10.3390/w17203006
Chicago/Turabian StyleDashkevych, Oleg, and Mashor Housh. 2025. "Management of Conventional and Non-Conventional Water Sources: A Systematic Literature Review" Water 17, no. 20: 3006. https://doi.org/10.3390/w17203006
APA StyleDashkevych, O., & Housh, M. (2025). Management of Conventional and Non-Conventional Water Sources: A Systematic Literature Review. Water, 17(20), 3006. https://doi.org/10.3390/w17203006