Skip to main content

Water woes: the institutional challenges in achieving SDG 6

Abstract

Background

Sustainable Development Goal (SDG) 6 envisions a future where everyone has access to clean water and sanitation. Yet, as 2030 looms closer, the complexity of achieving this target becomes apparent, with issues far surpassing basic water infrastructure and utility challenges. The underlying problems lie in broader spheres such as governance, policymaking, and financing.

Main body

The global landscape of water management is marked by complexities that transcend the operational troubles of water utilities. Financial sustainability is a monumental task. And while it is true that water utilities struggle with revenue generation, the broader picture reveals systemic challenges. The true cost of water provision often extends to ecosystem services such as watershed protection. Often, these services are not internalized in the revenue models of utilities but are typically subsidized by governments or simply not considered. Balancing affordability for users with cost recovery for service providers, however, is not just an arithmetic exercise. It is also a question of equitable policies. Non-revenue water (NRW), resulting from physical losses such as leaks, theft, and inaccurate [or lack of] metering, exacerbates existing financial strain. Annual NRW losses are estimated at an astonishing 126 billion cubic meters, costing roughly USD 39 billion. But at the most fundamental level of achieving SDG 6 is misgovernance. Effective water governance demands consistent policies, coherent collaboration among diverse stakeholders, and comprehensive strategies that cater to specific regional contexts. Current models often suffer from fragmented policies, inadequate public-private partnerships, and weak engagement mechanisms. A glaring gap exists between academic advancements in water management and their practical implementation in policymaking. Moreover, international cooperation, while vital, reveals an unequal landscape in knowledge exchange. Knowledge transfer is often skewed, favoring dominant nations while sidelining voices from the Global South. This emphasizes the need for an inclusive, equitable, and context-specific global cooperation model.

Conclusion

The road to realizing SDG 6 is multifaceted, and while on-the-ground solutions are essential, the real success lies in addressing the foundational challenges. This requires innovative financial solutions, reimagining water governance structures, and ensuring all voices, especially from the Global South, are heard and integrated into global policies. As 2030 nears, it is the synergy of governance, finance, and technology that will ultimately make clean water and sanitation a reality for all.

Introduction

In 2015, the leaders of UN Member states united behind an audacious vision: achieving 17 Sustainable Development Goals (SDGs) aimed at ending poverty, protecting the planet and improving the lives and prospects of everyone, everywhere. Slated for completion by 2030, the stark and sobering disconnect between ambition and reality becomes apparent as we approach the halfway mark. Particularly prominent is the lack of progress on SDG 6. This goal not only prioritizes the provision of drinking water, sanitation, and hygiene (WaSH) services, but also emphasizes the sustainable management of water resources globally. The vision captures essential advancements related to water access, pollution reduction, management of water across boundaries, enhancement of water use efficiency, and curtailment of unsustainable water withdrawals.

Despite noble intentions, nearly 30% of humanity still lacks access to safely managed drinking water [1], A staggering 1.7 billion people lack basic sanitation [1]. Regardless of economic status, pollution continues to deteriorate water quality in numerous rivers across Latin America, Africa, and Asia [2]. Globally, vital and delicate wetlands are shrinking at an alarming rate of 0.2% annually [3]. Progress on transboundary cooperation has remained limited, and in some areas where hydropower is growing in importance, geopolitical tensions have increased. Approximately half of the world’s population experience severe water scarcity for at least 1 month each year due to climatic extremes and land degradation, among other factors [4]. Concurrently, growing global population, along with increased industrialization, urbanization, and shifting consumption patterns, intensifies the demand for water resources worldwide [5]. These challenges are set against the backdrop of rapid global change.

In perspective: climate change, SDG 6, and institutional failures

Climate change undeniably influences the water cycle, increasing evaporation and altering precipitation patterns across regions [4]. For example, climate-induced changes in the water cycle are exacerbating water shortages in arid, semi-arid, and Mediterranean regions by inducing long-term declines in annual precipitation [6, 7] and increasing the threats posed by salinization [8, 9]. These not only make water availability less predictable but also amplify existing challenges. However, while climate change contributes to the unpredictability, it is crucial to understand that many water crises are primarily products of mismanagement and lack of political will, rather than direct outcomes of climate change.

Droughts, floods, and other hydrological phenomena have been part and parcel of our planet’s history. The current observed fluctuations over the past 5 years, however, were unprecedented even by 2018’s consensus [10]. But, even though climate change does aggravate these hydrological phenomena, in the context of domestic water supply, it is management and political prioritization that have a more prominent role to play. It is vital to acknowledge that a vast majority of nations use less than 10% of their total water for domestic purposes. In a well-managed system with political backing, this should, in principle, suffice to provide a significant portion of the population with clean drinking water. Sadly, this is not the case. This suggests that the core issue might lie more in governance than in climate change.

Consider the melting of non-polar glaciers, notably in the Hindu-Kush Himalayas. While their accelerated retreat due to rising air temperatures and black carbon deposition raises long-term water availability concerns, in the short-to-medium term, glacier-melt has augmented water supply for millions [11]. Such nuances emphasize the need to approach water challenges with a balanced perspective, acknowledging benefits where they arise while planning for future risks.

The 2022 flood in Pakistan provides a case in point. While it was triggered by heavy rainfall, the primary contributor to its devastating impact was the lack of disaster prevention planning and execution [12]. Similar climatic events in countries such as India and Bangladesh would likely have resulted in significantly less damage, owing to their enhanced preparedness. That is, relative to Pakistan’s. Furthermore, focusing solely on flooding obscures a critical issue. Many regions in Pakistan, like several other developing Asian nations, did not have access to “safe drinking water” even before the flood. Piped water, while accessible, often requires household-level treatment before consumption.

Another case in point is the 2023 dam failure in Libya. While Storm Daniel was undoubtedly a force to reckon with, it was the long-term negligence in the design, construction, and maintenance of the Darna and Mansour dams that rendered them vulnerable. Decades of neglect and poor upkeep culminated in the disaster that ensued. Thus, attributing the dam failures solely to climate change or Storm Daniel might be an oversimplification.

Thus, while climate does play a role, it is critical to understand the multifaceted nature of water-related challenges, from systemic mismanagement to varying socio-economic realities and infrastructural disparities. Alongside addressing the tangible impacts of climate change (SDG 13), it is equally vital to tackle institutional challenges and prioritize effective water management for a holistic approach to achieving water security.

These issues extend beyond mere statistics and observations; they underline broken commitments, poor governance, and reluctance to work together in championing sustainable solutions. If we don’t quadruple our current progress rate for SDG6, billions will still lack access to clean water and sanitation by 2030 [13]. Yet, there is little evidence that any acceleration in effort is occurring or emerging [14]. Why has this occurred? In this Debate contribution, we outline inter-related institutional challenges that exist in pursuing SDG 6. These challenges relate to ensuring funding to build and sustain infrastructure, committing to sustainable management of water resources, and providing stronger governance needed to evoke change.

Institutional challenges

Challenge 1: Financial disenfranchisement

Underfunding

The financial gaps for achieving SDG 6 are considerable. Estimates suggest a global need ranging from USD 30 billion to a daunting USD 1.1 trillion per year [15]. Estimates based on Integrated Assessment Models, which take into account the impacts of climate change, range between USD 445 and USD 885 billion annually [15]. Achieving universal access to WaSH services alone necessitates an annual investment of USD 28.4 billion [16]. Aiming for safely managed services would triple these costs to USD 86.9 billion. The typical funding streams – Tariffs, Taxes, and Transfers – are generally unable to cover the full costs required for ensuring the provision of adequate WaSH services, let alone capacity expansions driven by growing demand [17,18,19].

The funding landscape also reveals significant regional disparities among end users. Much of the Global South grapples with funding shortages for critical water projects [20]. For instance, in Southern Africa, there’s a noticeable deficit in investments for WaSH services [21]. This shortfall intensifies existing access inequities and contributes to adverse health outcomes [22]. The African water sector is further hamstrung by the chronic underpricing of water. Tariffs, in principle, should help narrow the expenditure gap. But often, tariffs barely cover costs, making it challenging to fund operations and maintenance (O&M) [23]. Paradoxically, water tariffs in Africa are already relatively high, even compared to other developing regions [24]. Thus, implementing higher tariffs may exacerbate water insecurity unless buttressed with measures that combat poverty [25].

It is important to acknowledge that while many discussions in the literature focus on the commodification of water supply and wastewater treatment, viewing these services merely as commercial enterprises overlooks their essential role as public goods. Such a perspective underscores the importance of state involvement, public investment, and state capacity to address social inequalities and ensure equitable access to these vital services.

Multilateral development banks (MDBs) partially plug the funding gaps in developing regions by providing official development assistance (ODA), which is aid from donor countries aimed at fostering development in regions identified as developing by the OECD [26]. ODA is delivered either directly from a donor country or through a multilateral agency. Over the last decade, MDBs provided over USD 15 billion for WaSH infrastructure worldwide [20]. However, the reported decreasing trend in ODA, down by 12% to USD 9.8 billion between 2015 and 2021, exacerbates the uncertainty of meeting the funding needs in areas with the greatest need and limited funding [27].

Conversely, much of the developed world generally enjoys better access to safe drinking water and high financial cost-recovery rates. Cost-recovery rates in the UK, France, Germany, and the Netherlands were close to or higher than 100% [23]. However, the Global North is not without challenges. Aging infrastructure, water contamination, and regional disparities persist [28, 29]. Areas with marginalized communities still face water issues. Over 2 million people in the United States, along with indigenous populations in Australia [30] and Canada, lack access to safe drinking water, indoor plumbing, or adequate wastewater disposal facilities [31]. The Flint, Michigan crisis underscores that even wealthy countries are not immune to systemic challenges causing public health emergencies linked to water quality [32,33,34]. U.S. water utilities are struggling with generally fixed and rising costs, while their typically variable revenue has been on a decline [35]. Such imbalance is making it increasingly difficult to maintain financial sustainability. In some European countries, the absence of metering results in water wastage and increased wastewater treatment costs [23].

Funding inequality

Inequality in funding further exacerbates these challenges. Funding often disproportionately favors urban areas, leaving rural regions, where the need may be greater, underfunded [20]. Economic instability and high levels of national debt can make it difficult for countries to secure additional funding for water and sanitation projects. Moreover, while the water sector does provide both public and private benefits, many cannot be easily monetized, which limits potential revenue streams [36]. The current financial system, with its macro and micro disparities, is ill-equipped to sufficiently fund crucial water investments [37]. Of the three financial mechanisms for funding water projects in both developed and developing economies – public, corporate, and project finance – only the project finance model allows global capital markets to invest in countries with non-exchangeable currencies. But the investment costs often outweigh the potential profit from water projects [37]. In urban settings, investments in water distribution are more economically feasible in high-density areas. However, as population density decreases towards the outskirts, the financial viability drops. Furthermore, residents in high-density areas frequently resist any increase in their water rates, which could help subsidize the expansion of the system to the less economically viable zones.

Structural and operational inefficiencies, combined with lack of institutional capacity, limited data, analytical tools, and sector knowledge, add to the problem. Additionally, there is an evident mismatch in the supply and demand sides of finance, which discourages potential commercial investors due to high initial investment needs and extended payback periods [36].

Financial inequalities intensify these challenges. Richer areas usually have better funding, modern technology, and skilled workers. This allows for more advanced or higher-quality water systems. Meanwhile, poorer regions face outdated infrastructure, limited funds, and weak investment prospects. This growing gap does not just limit equal water access. It also blocks system upgrades and new water solutions for the most needy.

The transboundary nature of many water resources further complicates financing. There is a perceived high risk in investing in transboundary water projects, with the benefits often misunderstood or undervalued, leading to insufficient resources for water cooperation at this level [38, 39].

International aid and ODA, while useful, are not a panacea. Often, such aid brings about long-term sustainability issues, with loans carrying conditions that might not align with a nation’s unique water and sanitation needs. Mismanagement, corruption, lack of political will, and intricate regulations further impede the impact of these funds, slowing project implementation and escalating costs. Ranging from high-level abuses to petty bribery, corruption also results in substandard infrastructure, and inequitable resource distribution. These challenges not only make water services unaffordable for many but also perpetuate cycles of poverty and deepen social disparities.

Challenge 2. Financial sustainability

One pervasive challenge for water utilities worldwide is financial sustainability [40]. Water utilities struggle to generate sufficient revenue to cover O&M costs [19]. The true cost of water supply also encompasses the payment for ecosystem services (PES) such as watershed protection, reforestation, stream bank protection, and increased infiltration, which are typically subsidized by governments, when implemented. The issue is compounded by the complexity of balancing affordable tariffs for consumers while ensuring cost recovery for service providers [19, 23].

It can be argued, however, that the core issue in financing water utilities is not the scarcity of funds, but the lack of sustainable financing models to cover both capital expenditure (capex) and operational expenditure (opex). Despite some utilities receiving capex funding from MDBs, without proper models, operational activities suffer in the long run. Donors are eager to provide funds for utilities with a solid financing model, as observed with Cambodia’s Phnom Penh Water Supply Authority [41]. The majority of utilities, however, lack such models. Essential long-term water and sanitation services are achievable, and households should pay for these services either through tariffs or taxes, with only genuinely needy households receiving subsidies.

On balance, it can be argued that capital should be readily available for projects that are “bankable”. Phnom Penh Water Supply Authority’s success over 25 years with a strong governance and financial model is an example [42]. Thus, utilities lacking a credible financial model face challenges in attracting capital investment. However, this does not mean that addressing continuous and systemic waste is not essential for enhancing or at least increasing the financial sustainability of water utilities.

Non-revenue water (NRW), characterized by physical losses from leaks, water theft, inaccurate metering, etc., further contribute to the chronic financial unsustainability in the water sector. Current estimates report NRW losses of 126 billion cubic meters annually, incurring a substantial cost of USD 39 billion [43]. Globally, the median level of NRW, expressed as a percentage of system input, is estimated at 40% (IQR 15%), ranging from 4% in Singapore to 83% in Armenia (Fig. 1A). The global median NRW is 69 liters per capita per day (Fig. 1B), demonstrating that NRW losses are a globally prevalent issue. Their high rates indicate the essential need for substantial investments in water infrastructure to reduce losses and ensure the financial sustainability of the water sector worldwide. These figures underline the urgency in addressing this issue, as it reflects not only significant economic losses but also grave inefficiencies in global water resources management.

Fig. 1
figure 1

Non-revenue water (NRW). A Global map of the level of NRW per country as a percentage of system input volume. Density histogram of NRW per country in liters per capita per day. In the density histogram, the vertical axis representing ‘probability density’ indicates the likelihood of observing different values of NRW per capita per day within the dataset. Specifically, for any given value on the horizontal axis, the height of the histogram at that point reflects how common or frequent that particular NRW value is in the dataset. This allows for a more nuanced understanding of the distribution of NRW across countries, showing not just the number of occurrences but the relative frequency of each occurrence, standardized across the entire range of data. Source of NRW data is ref. [43]

Technological innovations are crucial in reducing NRW by identifying system leaks and inaccuracies. Tools such as acoustic sensors, smart metering, and predictive analytics allow utilities to detect issues, educate consumers, and foresee potential failures. These advances lead to financial savings, improved water conservation, and reliable service.

NRW exerts significant financial strain on water utilities, amidst increasing water scarcity and aging infrastructure. NRW was the most important aspect influencing the financial sustainability of a water utility in Kenya [44]. The necessity for effective NRW reduction strategies in Malaysian water utilities was underscored to cater to the escalating water demand and bolster financial sustainability [45]. Reducing NRW has been shown to diminish environmental burdens and boost the sustainability of water supply systems in India [46]. Simply put, lost water is lost revenue. And lost revenue seriously undermines a water utility’s ability to provide reliable and affordable services.

In addition to NRW, the continuous upward trend in O&M costs compounds the financial woes faced by water utilities. By 2029, O&M costs are projected to surpass capital expenditure by 1.6 times [19]. A survey of 605 utilities from developing countries showed that a mere 17% of them covered their O&M costs and achieved sufficient surpluses [47]. It is inevitable that utilities need to explore measures to reduce costs and increase efficiency in order to remain viable in the years to come.

Challenge 3. Misgovernance

Weak governance

Water governance, especially in terms of policy coherence and collaboration among governmental, private and NGO actors with asymmetric rights and responsibilities as well as differing interests and agendas [48], are recognized as crucial for managing water resources under different contexts. Paradigms such as Integrated Water Resources Management (IWRM) (SDG Target 6.5), is considered as crucial for adapting to the multifaceted challenges posed by climate change, urbanization, and shifting demographics. Yet, status quo understanding reveals a complex landscape of challenges across nations and cities, affecting both developed and developing regions that make its translation and adoption very difficult [49].

In many countries, from India to Mexico, Chief Executives of water utilities have short average tenures of about 18 months. Many lack technical or utility management backgrounds. Longer tenures of 6 years, split into two 3-year terms with specific key performance indicators, could solve around 60% of the problems faced by such countries [42]. This is even at current funding levels [42]. Cities like Dhaka and São Paulo witnessed improved utility performance after making their utilities autonomous and hiring headhunted Chief Executives. Notably, São Paulo’s public sector owns the majority of utility shares, but the private sector appoints the CEO. This leads to improved water delivery and commercial financing [42].

Further, achieving SDG 6 requires strong public-private partnerships. Doing so requires leveraging private sector investments and bolstering governance, especially as the water sector is susceptible to “leakage”. Corruption, for example, not only hampers environmental and social outcomes but also deters vital investments. Thus, a collaborative approach between public, private, and civil society is pivotal to ensure transparency and efficiency in water infrastructure financing.

Context matters and countries develop what can be considered as unique water management and governance models. In Latin America, Chile’s market-driven model exhibits a lack of social participation due to lack of a more effective state regulation [50]. Mexico [51] and Brazil [52] seem to fare better in terms of community engagement. However, shared deficiencies across these countries emphasize concerns over financing, participatory mechanisms and gender and indigenous populations inclusivity in water governance.

Urban water governance challenges to meet SDG 6 are heightened by climate change effects. Focusing on Australia, Horne [53] emphasizes the importance of managing water demand and not simply focusing on supply. He underscores cost-effective demand reduction strategies that may be required to supplement more robust governance structures and enhanced prosecution of corruption if SDG goals are to be met.

A recent analysis on 200 cities [54], representing 95% of the global urban population, underlines the gravity of the urban water issue. A majority of global cities, especially in Africa, Asia, and Latin America, contend with significant deficits in water and sanitation governance frameworks. Targets related to basic drinking water supply, sanitation, solid waste management, and climate adaptability remain elusive for many. These underline the gap between current practices and the ideals set by the SDGs.

Policy challenges

The policy landscape remains rife with challenges in establishing and maintaining sustainable water systems. Islam and Islam [55] succinctly captures this challenge by highlighting the pervasive issue of “coordination gaps” in water quality management. This encompasses a broad spectrum of concerns, from policymaking to technology deployment, financing, monitoring, data management, and capacity building. A critical gap has been recognized between technical advancements and academic discourse versus the practical applications by policymakers [56]. This disconnect means that despite growing scientific literature supporting SDG 6, emphasis is still on water governance for surface and ground waters and wastewater collection and treatment, and emerging concepts like water security, water-energy-food nexus and reused water for potable use [57] are still in nascent stages. This, inevitably, leads to a policy lag, which underscores the need to bridge the divide between science and policy for more effective water governance frameworks.

International cooperation

Given the global nature of water challenges, international cooperation remains the cornerstone in achieving SDG 6. Bibliometric analysis reveals a concerning trend [56]. While collaborations amongst authors from dominant countries like the USA and UK are frequent, ties amongst authors from the Global South are sparse. This underlines an uneven playing field in knowledge exchange and cooperation. Moreover, the significance of indigenous and local knowledge in achieving water sustainability has to be studied much further [58]. The rare partnerships between Global South nations highlight a systemic imbalance where solutions are often driven by wealthier countries, neglecting culturally specific insights. With the UN SDGs emphasizing the integration of indigenous knowledge systems, international cooperation becomes critical to assimilating knowledge and information into mainstream water governance across countries.

The path towards achieving SDG 6 remains convoluted, marked by weak governance, policy challenges, and less-than-optimal international cooperation. Yet, it is crucial to remember that SDG 6 is not just about water. It is also about establishing sustainable ecosystems, ensuring public health, and building resilient urban infrastructures. Historically, policies, legal and regulatory frameworks and collaboration among institutions at different administrative levels have addressed water crises globally if effectively applied [59]. To do so will require a reinvigorated commitment to strengthening governance structures, bridging the policy gap, and fostering meaningful international collaborations.

Outlook

Achieving SDG 6 in view of the challenges that we outlined here demands global, coordinated innovation and action. Proper tariffs promote conservation, fund infrastructure improvements, and ensure system resilience. Capacity constraints in low- and middle-income countries need greater attention [60, 61]. Investing more in both fundamental and applied research will promote water management innovations [62, 63]. The notable funding shortfall, intensified by disparities in resource allocation and high non-revenue water losses, emphasizes the need for diversified financial strategies. Embracing innovative financial tools, including impact investments, green bonds, blue bonds, and other sustainable finance instruments [64] is essential. However, these tools must not exacerbate existing socio-ecological inequalities. International aid, while crucial, should be tailored to recipient nations’ specific needs [65], emphasizing transparency, accountability, and capacity-building without increasing financial strain or social injustice.

Recognizing water as a fundamental right is imperative. The true potential of sustainable finance will be realized by aligning it with economic policies that account for externalities [37]. Moreover, comprehensive investment in infrastructure and technological innovation are paramount to achieving financial sustainability. The collective aim to overcome these barriers and realize universal access to water and better sanitation by 2030 hinges on this multifaceted, collaborative approach. This approach needs to combine robust governance (including sustained attention to corrupt practices), innovative financing and appropriate technology.

In the face of climate change’s growing impact on water scarcity and quality, there are practical and positive steps we can take. Firstly, we need to focus on sustainable water management in water stressed regions, promoting water conservation and appropriate distribution. This includes harnessing traditional water harvesting methods and adopting innovative storage solutions. Secondly, addressing water contamination is crucial. We should invest in resilient wastewater treatment facilities and improve early warning systems to safeguard populations against extreme weather events. Recognizing the interconnected nature of these challenges, we must address their root causes. This involves combatting deforestation and pollution, which harm water quality and availability. Collaboration on a global scale, with particular attention to vulnerable low-income countries, is essential. This can be achieved through technology sharing, capacity-building, and financial support. Lastly, educating and empowering communities is vital. However, we must remember that while education can be a catalyst for change, many individuals with education might misuse their knowledge to manipulate the system. Hence, while building knowledge and tools at the local level is essential, addressing the unequal power dynamics is equally crucial to truly promote and support resilience.

Addressing the complex challenges of water governance is imperative as we look towards an increasingly non-stationary future [66]. Adopting context-aware governance models, tailored to regional nuances, is paramount. Bridging the academic-research and policy-implementation divide, utilizing concepts like the water-energy-food nexus, will address current shortcomings. Inclusive international cooperation, promoting knowledge exchange while respecting local intricacies, is fundamental for collaborative and transformative water governance.

Availability of data and materials

Not applicable.

Abbreviations

UN:

United Nations

SDG:

Sustainable Development Goals

NRW:

Non-revenue water

WaSH :

Water, Sanitation, and Hygiene

O&M:

Operations and Maintenance

Capex:

Capital Expenditure

Opex:

Operational Expenditure

MDBs:

Multilateral Development Banks

ODA:

Official Development Assistance

PES:

Payment for Ecosystem Services

IWRM:

Integrated Water Resources Management

CEO:

Chief Executive Officer

References

  1. State of the world’s drinking water: an urgent call to action to accelerate progress on ensuring safe drinking water for all [Internet]. [cited 2023 Oct 2]. Available from: https://iris.who.int/handle/10665/363704.

  2. UNEP. A Snapshot of the World’s Water Quality: Towards a Global Assessment [Internet]. Available from: https://wedocs.unep.org/20.500.11822/19524.

  3. Davidson NC, Finlayson CM. Updating global coastal wetland areas presented in Davidson and Finlayson (2018). Mar Freshw Res. 2019;70(8):1195–200. https://doi.org/10.1071/MF19010.

    Article  Google Scholar 

  4. Intergovernmental Panel on Climate Change. Climate Change 2021 – The Physical Science Basis [Internet]. Cambridge University Press; 2023. [cited 2023 Oct 2]. Available from: https://doi.org/10.1017/9781009157896.

  5. Vörösmarty CJ, Green P, Salisbury J, Lammers RB. Global Water Resources: Vulnerability from Climate Change and Population Growth. Science. 2000;289(5477):284–8. https://doi.org/10.1126/science.289.5477.284.

    Article  PubMed  ADS  Google Scholar 

  6. Overpeck JT, Udall B. Climate change and the aridification of North America. Proc Natl Acad Sci. 2020;117(22):11856–8. https://doi.org/10.1073/pnas.2006323117.

    Article  CAS  PubMed  PubMed Central  ADS  Google Scholar 

  7. Brogli R, Sørland SL, Kröner N, Schär C. Causes of future Mediterranean precipitation decline depend on the season. Environ Res Lett. 2019;14(11):114017. https://doi.org/10.1088/1748-9326/ab4438.

    Article  ADS  Google Scholar 

  8. Lassiter A. Rising seas, changing salt lines, and drinking water salinization. Curr Opin Environ Sustain. 2021;50:208–14. Available from: https://www.sciencedirect.com/science/article/pii/S187734352100066X

    Article  Google Scholar 

  9. Shammi M, Rahman MM, Bondad SE, Bodrud-Doza M. Impacts of Salinity Intrusion in Community Health: A Review of Experiences on Drinking Water Sodium from Coastal Areas of Bangladesh. Healthc. 2019;7(1):50. Available from: https://doi.org/10.3390/healthcare7010050.

  10. Summary for Policymakers of IPCC Special Report on Global Warming of 1.5°C approved by governments — IPCC [Internet]. [cited 2023 Oct 20]. Available from: https://www.ipcc.ch/sr15.

  11. Rinzin S, Zhang G, Sattar A, Wangchuk S, Allen SK, Dunning S, et al. GLOF hazard, exposure, vulnerability, and risk assessment of potentially dangerous glacial lakes in the Bhutan Himalaya. J Hydrol. 2023;1(619):129311.

    Article  Google Scholar 

  12. Stringer LC, Mirzabaev A, Benjaminsen TA, Harris RMB, Jafari M, Lissner TK, et al. Climate change impacts on water security in global drylands. One Earth. 2021;4(6):851–64.

    Article  ADS  Google Scholar 

  13. Merid MW, Alem AZ, Chilot D, Belay DG, Kibret AA, Asratie MH, et al. Impact of access to improved water and sanitation on diarrhea reduction among rural under-five children in low and middle-income countries: a propensity score matched analysis. Trop Med Health. 2023;5(1):1–10. https://doi.org/10.1186/s41182-023-00525-9.

    Article  Google Scholar 

  14. Allen C, Malekpour S. Unlocking and accelerating transformations to the SDGs: a review of existing knowledge. Sustain Sci. 2023;18(4):1939–60.

    Article  Google Scholar 

  15. Kulkarni S, Hof A, Ambrósio G, Edelenbosch O, Köberle AC, van Rijn J, et al. Investment needs to achieve SDGs: An overview. PLOS Sustain Transform. 2022;1(7):e0000020. https://doi.org/10.1371/journal.pstr.0000020.

    Article  Google Scholar 

  16. Hutton G, Varughese M. The costs of meeting the 2030 sustainable development goal targets on drinking water, sanitation and hygiene:Summary Report Other Research. The World Bank; 2016. p. 24. https://doi.org/10.1596/K8632.

    Book  Google Scholar 

  17. Pories L, Fonseca C, Delmon V. Mobilising Finance for WASH: Getting the Foundations Right. Water. 2019;11(11):2425. [cited 2023 Oct 2]. Available from: https://doi.org/10.3390/w11112425.

  18. Danert K, Hutton G. Shining the spotlight on household investments for water, sanitation and hygiene (WASH): let us talk about HI and the three ‘T’s. J Water Sanit Hyg Dev. 2020;10(1):1–4. https://doi.org/10.2166/washdev.2020.139.

    Article  Google Scholar 

  19. Libey A, Adank M, Thomas E. Who pays for water? Comparing life cycle costs of water services among several low, medium and high-income utilities. World Dev. 2020;1(136):105155.

    Article  Google Scholar 

  20. Heidler A, Nesi M, Nikiema J, Lüthi C. Multilateral development banks investment behaviour in water and sanitation: Findings and lessons from 60 years of investment projects in Africa and Asia. J Water, Sanit Hyg Dev [Internet]. 2023;13(5):362–74. [cited 2023 Sep 19]. Available from: https://doi.org/10.2166/washdev.2023.004.

  21. Tseole NP, Mindu T, Kalinda C, Chimbari MJ. Barriers and facilitators to water, sanitation and hygiene (WaSH) practices in southern Africa: a scoping review. PLoS One. 2022;17(8):e0271726. https://doi.org/10.1371/journal.pone.0271726.

    Article  CAS  PubMed  PubMed Central  Google Scholar 

  22. Kamara JK, Galukande M, Maeda F, Luboga S, AMN R. Understanding the Challenges of Improving Sanitation and Hygiene Outcomes in a Community Based Intervention: A Cross-Sectional Study in Rural Tanzania. Int J Environ Res Public Heal. 2017;14(6):602. Available from: https://www.mdpi.com/1660-4601/14/6/602/htm

    Article  Google Scholar 

  23. Hukka JJ, Katko TS. Appropriate pricing policy needed worldwide for improving water services infrastructure. J Am Water Works Assoc. 2015;107(1):E37–46. https://doi.org/10.5942/jawwa.2015.107.0007.

    Article  Google Scholar 

  24. World Bank. Africa’s Infrastructure : A Time for Transformation [Internet]. Herndon, UNITED STATES: World Bank Publications; 2009. Available from: https://www.worldbank.org/en/news/feature/2009/11/12/transforming-africasinfrastructure.

  25. Stoler J, Pearson AL, Staddon C, Wutich A, Mack E, Brewis A, et al. Cash water expenditures are associated with household water insecurity, food insecurity, and perceived stress in study sites across 20 low- and middle-income countries. Sci Total Environ [Internet]. 2020;716:135881. Available from: https://doi.org/10.1016/j.scitotenv.2019.135881.

  26. Erdem TG. Official development assistance (ODA). Aid Dynam Sustain Develop. 2020:1–13. Available from: https://link.springer.com/referenceworkentry/10.1007/978-3-319-71067-9_98-1

  27. Blueprint for Acceleration: Sustainable Development Goal 6 Synthesis Report on Water and Sanitation 2023 | UNWater [Internet]. [cited 2023 Oct 2]. Available from: https://www.unwater.org/publications/sdg-6-synthesis-report-2023.

  28. Collier SA, Deng L, Adam EA, Benedict KM, Beshearse EM, Blackstock AJ, et al. Estimate of Burden and Direct Healthcare Cost of Infectious Waterborne Disease in the United States - Volume 27, Number 1—January 2021 - Emerging Infectious Diseases journal - CDC. Emerg Infect Dis [Internet]. 2021;27(1):140–9. [cited 2023 Sep 22]. Available from: https://doi.org/10.3201/eid2701.190676.

  29. Wu J, Cao M, Tong D, Finkelstein Z, Hoek EMV. A critical review of point-of-use drinking water treatment in the United States. npj Clean Water 2021 41 [Internet]. 2021;4(1):1–25. [cited 2023 Sep 22]. Available from: https://doi.org/10.1038/s41545-021-00128-z.

  30. Wyrwoll PR, Manero A, Taylor KS, Rose E, Quentin GR. Measuring the gaps in drinking water quality and policy across regional and remote Australia npj. Clean Water. 2022;5(1):1–14. Available from: https://www.nature.com/articles/s41545-022-00174-1

    Google Scholar 

  31. Quentin Grafton R, Biswas AK, Bosch H, Fanaian S, Gupta J, Revi A, et al. Goals, progress and priorities from Mar del Plata in 1977 to New York in 2023. Nat Water. 2023;1(3):230–40. [cited 2023 Oct 20]. Available from: https://doi.org/10.1038/s44221-023-00041-4.

  32. Pieper KJ, Tang M, Edwards MA. Flint water crisis caused by interrupted corrosion control: investigating “ground zero” home. Environ Sci Technol. 2017;51(4):2007–14. https://doi.org/10.1021/acs.est.6b04034.

    Article  CAS  PubMed  ADS  Google Scholar 

  33. Masten SJ, Davies SH, SP ME. Flint Water Crisis: What Happened and Why? J Am Water Works Assoc. 2016;108(12):22–34. https://doi.org/10.5942/jawwa.2016.108.0195.

    Article  PubMed  PubMed Central  Google Scholar 

  34. Sadler RC, Highsmith AR. Rethinking Tiebout: the contribution of political fragmentation and racial/economic segregation to the Flint water crisis. Environ Justice. 2016;9(5):143–51. https://doi.org/10.1089/env.2016.0015.

    Article  Google Scholar 

  35. Ali M, Wang J, Himmelberger H, Thacher J. An Economic Perspective on Fiscal Sustainability of U.S. Water Utilities: What We Know and Think We Know. Water Econ Policy. 2021;07(01):2150001. https://doi.org/10.1142/S2382624X21500016.

    Article  Google Scholar 

  36. OECD. Financing a Water Secure Future [Internet]. 2022. 138 p. Available from: https://doi.org/10.1787/22245081.

  37. Martini MJ. Financing instruments and the ecology of the financial system. Financ Invest Water Secur Recent Dev Perspect. 2022;1:79–100.

    Article  Google Scholar 

  38. UNECE. Funding and financing of transboundary water cooperation and basin development | [Internet]. [cited 2023 Oct 2]. Available from: https://unece.org/environment-policy/publications/funding-and-financing-transboundarywater-cooperation-and-basin.

  39. UNESCO. Progress on transboundary water cooperation: global status of SDG indicator 6.5.2 and acceleration needs, 2021 [Internet]. Available from: https://unesdoc.unesco.org/notice?id=p::usmarcdef_0000378914.

  40. Reis N. Between development and banking: the KfW development Bank in Latin America’s water sector. Water Int. 2022;47(5):810–36. https://doi.org/10.1080/02508060.2022.2105533.

    Article  Google Scholar 

  41. Biswas AK, Sachdeva PK, Tortajada C. Phnom Penh Water Story. 2021. [cited 2023 Sep 30]; Available from: https://doi.org/10.1007/978-981-33-4065-7.

  42. Biswas AK, Tortajada C. Global crisis in water management: Can a second UN Water Conference help? River [Internet]. 2023;2(2):143–8. https://doi.org/10.1002/rvr2.40.

    Article  Google Scholar 

  43. Liemberger R, Wyatt A. Quantifying the global non-revenue water problem. Water Supply. 2018;19(3):831–7. https://doi.org/10.2166/ws.2018.129.

    Article  Google Scholar 

  44. Akinyi AM, Odundo PA. Revenue Generation Aspects That Influence Financial Sustainability of Public Water Utilities in Kenya: The Case of Homa Bay Water and Sewerage Company Limited. In 2018. Available from: https://doi.org/10.20849/abr.v3i2.370.

  45. Putri BN, Ahmad I, Abdullah N. Water Distribution and Non-Revenue Water Management Scenario in Asian countries: Malaysian Perspective. J Adv Res Appl Sci Eng Technol. 2021;25(1):94–105. Available from: https://doi.org/10.37934/araset.25.1.94105.

  46. Negi R, Singh VK, Chandel MK. Effect of Non-Revenue Water Reduction in the Life Cycle of Water–Energy Nexus: A Case Study in India In 2020. Available from: https://api.semanticscholar.org/CorpusID:234328671.

  47. Leigland J, Tremolet S, Ikeda J. Achieving Universal Access to Water and Sanitation by 2030: The Role of Blended Finance. Achiev Univers Access to Water Sanit by 2030 [Internet]. 2016 Aug [cited 2023 Oct 2]; Available from: http://hdl.handle.net/10986/25111

  48. Wang RY, van Rijswick M, Dai L. Improving connectivity in water governance: the implementation of water cooperation mechanisms in disparate political and social contexts. Int J Water Resour Dev. 2022;38(4):545–53. https://doi.org/10.1080/07900627.2022.2071848.

    Article  Google Scholar 

  49. Biswas AK. Integrated Water Resources Management: A Reassessment. Water Int. 2004;29(2):248–56. https://doi.org/10.1080/02508060408691775.

    Article  Google Scholar 

  50. Budds J. Securing the market: water security and the internal contradictions of Chile’s water code. Geoforum. 2020;1(113):165–75.

    Article  Google Scholar 

  51. Wilder M. Water governance in Mexico. Ecol Soc. 2010;15(2) Available from: http://www.jstor.org/stable/26268136

  52. Costa MM, e., Neto S. Exploratory analysis of the water governance frameworks regarding the OECD principles in two river basins in Brazil and Portugal. Util. Policy. 2023;1(82):101556.

    Google Scholar 

  53. Horne J. Water demand reduction to help meet SDG 6: learning from major Australian cities. Int J Water Resour Dev. 2020;36(6):888–908.

    Article  Google Scholar 

  54. Grison C, Koop S, Eisenreich S, Hofman J, Chang I-S, Wu J, et al. Integrated water resources Management in Cities in the world: global challenges. Water Resour Manag. 2023;37(6):2787–803. https://doi.org/10.1007/s11269-023-03475-3.

    Article  Google Scholar 

  55. Islam MA, Islam SL. Impact of climate change on water quality and public policy approach to reduce uncertainty and risk. Handbook Water Purity Qual. 2021:57–75.

  56. Basu M, Dasgupta R. Where do we stand now? A bibliometric analysis of water research in support of the sustainable development goal 6, vol. 13. Water (Switzerland); 2021. p. 24.

  57. Tortajada C, van Rensburg P. Drink more recycled wastewater. Nat. 2021;577(7788):26–8. Available from: https://www.nature.com/articles/d41586-019-03913-6

    Article  ADS  Google Scholar 

  58. Basu M, Dasgupta R. Indigenous and local water knowledge. In: Values and Practices. Indigenous and Local Water Knowledge. Values and Practices; 2023. p. 1–326.

    Chapter  Google Scholar 

  59. Nath S, Vyas JN, Deogade RB, Chandra P. Integrated water resources Management in Developing Nation: status and challenges toward water sustainability. In: The Route Towards Global Sustainability. Challenges and Management Practices; 2023. p. 367–78.

    Chapter  Google Scholar 

  60. UN-Water GLAAS 2019: National systems to support drinking-water, sanitation and hygiene - Global status report 2019 | UN-Water [Internet]. [cited 2023 Oct 20]. Available from: https://www.unwater.org/publications/un-water-glaas-2019-national-systems-support-drinking-water-sanitation-and-hygiene

  61. Weak systems and funding gaps jeopardize drinking-water and sanitation in the world’s poorest countries [Internet]. [cited 2023 Oct 20]. Available from: https://www.who.int/news/item/28-08-2019-weak-systems-and-funding-gaps-jeopardize-drinking-water-and-sanitation-in-the-world’s-poorest-countries

  62. UN-Water GLAAS 2017: Financing universal water, sanitation and hygiene under the Sustainable Development Goals | UN-Water [Internet]. [cited 2023 Oct 20]. Available from: https://www.unwater.org/publications/un-water-glaas-2017-financing-universal-water-sanitation-and-hygiene-under-sustainable

  63. Utilities of the Future: How to build universal and resilient water supply and sanitation systems [Internet]. [cited 2023 Oct 20] Available from: https://blogs.worldbank.org/water/utilities-future-how-build-universal-and-resilient-water-supply-and-sanitation-systems

  64. Bosmans P, de Mariz F. The Blue Bond Market: A Catalyst for Ocean and Water Financing J Risk Financ Manag. 2023, 2023 16(3):184 Available from: https://www.mdpi.com/1911-8074/16/3/184/htm

  65. Wolff P. The 2030 agenda and capital market integration in ASEAN. In: Sustainable Development Goals and Pandemic Planning: Role of Efficiency Based Regional Approaches; 2022. p. 543–65.

    Chapter  Google Scholar 

  66. Milly PCD, Betancourt J, Falkenmark M, Hirsch RM, Kundzewicz ZW, Lettenmaier DP, et al. Stationarity Is Dead: Whither Water Management? Science. 2008;319(5863):573–4. https://doi.org/10.1126/science.1151915.

    Article  CAS  PubMed  Google Scholar 

Download references

Acknowledgements

Not applicable.

Funding

The authors declare no specific funding utilized in the conduct of this research.

Author information

Authors and Affiliations

Authors

Contributions

JE wrote the original first draft and generated Fig. 1. All authors contributed to writing the subsequent drafts and approved the final manuscript.

Corresponding author

Correspondence to Jaivime Evaristo.

Ethics declarations

Ethics approval and consent to participate

Not applicable.

Consent for publication

Not applicable.

Competing interests

The authors declare that they have no competing interests.

Additional information

Publisher’s Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Rights and permissions

Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.

Reprints and permissions

About this article

Check for updates. Verify currency and authenticity via CrossMark

Cite this article

Evaristo, J., Jameel, Y., Tortajada, C. et al. Water woes: the institutional challenges in achieving SDG 6. Sustain Earth Reviews 6, 13 (2023). https://doi.org/10.1186/s42055-023-00067-2

Download citation

  • Received:

  • Accepted:

  • Published:

  • DOI: https://doi.org/10.1186/s42055-023-00067-2