Hostname: page-component-586b7cd67f-l7hp2 Total loading time: 0 Render date: 2024-11-27T15:15:55.395Z Has data issue: false hasContentIssue false

Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective

Published online by Cambridge University Press:  06 November 2023

Guangtao Fu*
Affiliation:
Centre for Water Systems, University of Exeter, Exeter, United Kingdom
Siao Sun
Affiliation:
Key Laboratory of Regional Sustainable Development Modelling, Institute of Geographical Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing, China
Lan Hoang
Affiliation:
IBM Research, Hartree Centre, Warrington, United Kingdom
Zhiguo Yuan
Affiliation:
School of Energy and Environment, City University of Hong Kong, Kowloon Tong, Hong Kong
David Butler
Affiliation:
Centre for Water Systems, University of Exeter, Exeter, United Kingdom
*
Corresponding author: Guangtao Fu; Email: [email protected]
Rights & Permissions [Opens in a new window]

Abstract

The potential of artificial intelligence (AI) in water management is widely recognised by research and practice communities alike, with an increasing number of applications showed tackling water supply, stormwater and wastewater management challenges. However, there is a critical knowledge gap in understanding the fundamental role of AI in the development of urban water infrastructure (UWI). This review aimed to provide an analysis of how AI could be aligned to support the future development of UWI systems. Four types of AI analytics – descriptive, diagnostic, predictive and prescriptive – are discussed and linked to the improvement in the performance of UWI systems from three categories: reliability, resilience and sustainability. It is envisioned that AI technology will play a pivotal role in UWI transitioning to the future through underpinning the five development pathways: decentralisation, circular economy, greening, decarbonisation and automation. The barriers in improving AI adoption in the real world are also highlighted from four dimensions: cyber-physical infrastructure, institutional governance, social-economic systems and technological development in wider society. Embedding AI in the development pathways and tackling the barriers can ensure that AI-empowered systems are deployed in an equitable and responsible way to improve the resilience and sustainability of future UWI systems.

Type
Overview Review
Creative Commons
Creative Common License - CCCreative Common License - BY
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (http://creativecommons.org/licenses/by/4.0), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited.
Copyright
© The Author(s), 2023. Published by Cambridge University Press

Impact statements

The development of urban water infrastructure (UWI) has been driven by the evolving needs of customers, society and the environment but now faces a number of profound challenges such as climate change, ageing assets, stringent regulations, increasing demands and inadequate investment. Artificial Intelligence (AI), a widely recognised disruptive technology, is shaping an increasing range of sectors such as healthcare and banking, however, there is a critical knowledge gap in understanding how AI will enhance the performance of water systems and revolutionise the future development of water systems in practice. This review provides an analysis of how AI could be aligned to support the five development pathways: decentralisation, circular economy, greening, decarbonisation and automation. This shows profound opportunities of AI application for the water sector in terms of how interventions should be developed and incorporated into the existing infrastructure system using AI-based methods and tools. In the meantime, practical implications and barriers arising from application of AI-based tools should be fully recognised and responsibly managed considering the following four dimensions: cyber-physical infrastructure, institutional governance, social-economic systems and technological development. Examples include data privacy, ethical and legal concerns, fear of job loss, lack of adequate skills, risks and unintended consequences from failure of AI systems. It is envisioned that trustworthy AI technologies will play a pivotal role in moving towards reliable, resilient and sustainable UWI systems.

Introduction

Urban water infrastructure (UWI) is fundamental in providing essential water and wastewater services and supporting the prosperity of cities. It has been evolving gradually to meet the increasing needs of society, ranging from water supply security, public health, flood management, social amenity, environmental protection, resources efficiency, ecological integrity and climate resilience (Brown et al., Reference Brown, Keath and Wong2009). However, UWI is now facing a wide range of chronic and acute threats such as increasing demands, stringent regulations, ageing, lack of investment, climate change and extreme weather events (Butler et al., Reference Butler, Ward, Sweetapple, Astaraie-Imani, Diao, Farmani and Fu2017). There is an urgent need to develop resilient and sustainable UWI which can maintain and improve service levels under future uncertainties and threats. A key approach to tackling these threats is provided through capitalising on the advances in information and communications technology (Lund et al., Reference Lund, Borup, Madsen, Mark, Arnbjerg-Nielsen and Mikkelsen2019) and AI.

Digitalisation of UWI systems has come a long way and now lies at the heart of the transformation towards the fourth revolution in the water sector, so called Water 4.0 (IWA, 2019; Daniel et al., Reference Daniel, Ajami, Castelletti, Savic, Stewart and Cominola2023; Rapp et al., Reference Rapp, Capener and Sowby2023). The advances in digital technologies enable the construction of the “cyber system” on top of the physical infrastructure system, which provides the following main functions: sensing and instrumentation, communications and networking, data management, cyber-security control and decision support. Supervisory control and data acquisition (SCADA) systems are widely adopted in water distribution systems, water treatment works and wastewater treatment plants (WWTPs) to provide real-time and in-situ monitoring of pressure, flow, water level and water quality indicators and remote control of actuators (e.g., pumps and valves). This was mainly driven by the pursuit of efficiency by water utilities and technological innovations in developing low-cost, low-maintenance and high-reliability sensors (Yuan et al., Reference Yuan, Olsson, Cardell-Oliver, van Schagen, Marchi, Deletic, Urich, Rauch, Liu and Jiang2019; Garrido-Baserba et al., Reference Garrido-Baserba, Corominas, Cortés, Rosso and Poch2020). However, systematic understanding of how UWI system performance can be enhanced through digitalisation is limited.

AI technologies have long been applied to UWI planning and management, however, there is a critical research gap in understanding how AI enhances the performance of UWI systems. Although there is no consensus on a single definition of AI, here it refers to the development of computer systems or machines to perform tasks that would normally require human intelligence such as learning, problem-solving, decision-making and perception (Xu et al., Reference Xu, Liu, Cao, Huang, Liu, Qian, Liu, Wu, Dong, Qiu, Qiu, Hua, Su, Wu, Xu, Han, Fu, Yin, Liu, Roepman, Dietmann, Virta, Kengara, Zhang, Zhang, Zhao, Dai, Yang, Lan, Luo, Liu, An, Zhang, He, Cong, Liu, Zhang, Lewis, Tiedje, Wang, An, Wang, Zhang, Huang, Lu, Cai, Wang and Zhang2021a; Richards et al., Reference Richards, Tzachor, Avin and Fenner2023). A broad suite of AI technologies have been developed for specific tasks such as system simulation, optimisation and prediction. Examples include evolutionary algorithms for optimal design and operation problems of water systems (Nicklow et al., Reference Nicklow, Reed, Savic, Dessalegne, Harrell, Chan-Hilton, Karamouz, Minsker, Ostfeld, Singh and Zechman2010; Li et al., Reference Li, Li, Chang, Sharma and Yuan2022a) and artificial neutral networks for flow and water quality prediction and anomaly detection (Fu et al., Reference Fu, Khu and Butler2010; Rodriguez-Perez et al., Reference Rodriguez-Perez, Leigh, Liquet, Kermorvant, Peterson, Sous and Mengersen2020). Machine learning, a subset of AI, allows systems to learn directly from data, examples and experience without pre-defined rules and is currently at the heart of AI implementation (The Royal Society, 2017) and has been applied to understand complex water systems and discover new insights from various data sets (Eggimann et al., Reference Eggimann, Mutzner, Wani, Schneider, Spuhler, Moy De Vitry, Beutler and Maurer2017; Liu et al., Reference Liu, Savic and Fu2023). The latest deep learning technology, which is a subset of machine-learning responsible for the current rise of AI, enable automatic feature extraction from raw data and have been used in a diverse range of urban water management problems, predominantly covering anomaly detection, prediction, asset assessment, operation, and planning and maintenance (Fu et al., Reference Fu, Jin, Sun, Yuan and Butler2022). However, AI applications in the water sector are based on a piecemeal approach and the insights gained from various technologies are not joined together to advance our understanding of how AI will revolutionise the development of UWI systems of the future.

This review addresses a key question: what is the fundamental role of AI in the development of resilient and sustainable cyber-physical UWI? It aims to provide a holistic synthesis of how AI could be aligned to support the development of UWI systems of the future. We first explore the ways that AI can enhance the performance of UWI systems in terms of three key aspects – reliability, resilience and sustainability, and then develop a routemap of how AI will shape the future development of UWI towards greater resilience and sustainability. This review shows that AI is indispensable in the digital transformation of the water sector and should be aligned to underpin five pathways -decentralisation, circular economy, greening, decarbonisation and automation (see Section 3) - through which the current UWI systems are transitioning towards the future. Given the vast number of AI papers in the literature, we first performed a search using the ISI Web of Knowledge on papers having one of the six AI-related terms (i.e., AI, machine learning, deep learning, data analytics, evolutionary algorithm and decision tree) and the word “water” in the title and then applied a snowballing method to identify the relevant papers in the references of previously identified papers. As a result, a total of 3,000 references were found from the literature search but following a careful review 85 references were selected for synthesis. A high proportion of references were excluded mainly due to (1) irrelevant application areas such as river basin water management, agriculture and hydrology, and (2) the same problems with different AI approaches. Note that this review is not intended to provide a comprehensive review of AI technologies and their application to specific water management problems as such reviews can be found in the literature (e.g., Eggimann et al., Reference Eggimann, Mutzner, Wani, Schneider, Spuhler, Moy De Vitry, Beutler and Maurer2017; Stewart et al., Reference Stewart, Nguyen, Beal, Zhang, Sahin, Bertone, Silva-Vieira, Castelletti, Cominola, Giuliani, Giurco, Blumenstein, Turner, Liu, Kenway, Savic, Makropoulos and Kossieris2018; Zounemat-Kermani et al., Reference Zounemat-Kermani, Matta, Cominola, Xia, Zhang, Liang and Hinkelmann2020; Fu et al., Reference Fu, Jin, Sun, Yuan and Butler2022; Garzón et al., Reference Garzón, Kapelan, Langeveld and Taormina2022).

How can AI improve urban water system performance?

This section first provides a general introduction of AI domains and their application to UWI systems, then explains the three categories of UWI system performance, and finally shows how the system performance could be improved via different types of AI analytics.

Types of AI and their applications to UWI systems

The definition and taxonomy of AI and its applications can vary widely across application areas. In this paper, we adopt the Joint Research Centre taxonomy (Samoili et al., Reference Samoili, Cobo, Gómez, De Prato, Martínez-Plumed and Delipetrev2020) which provides a useful reference for AI development, uptake and impacts. This AI taxonomy covers a wide range of core AI sub-domains and transversal areas. For the purpose of this paper, we do not include the transversal AI areas such as robots, AI services and philosophical considerations, which go beyond our direct aim of linking AI with UWI systems. The core AI can be divided into reasoning, planning, learning, communication and perception (Table 1). From the literature search, AI has a long history of intersecting urban water research, particularly in the area of planning, scheduling, optimisation and searching. In Table 1, we have shown examples of water applications that set out operation scheduling or optimise capacity expansion of urban water systems. Other AI domains of machine learning, natural language processing, computer vision and audio processing also present in water applications, such as in anomaly detection, water demand forecasting, flow forecasting, weather prediction, as well as other general water monitoring purposes (e.g., Eggimann et al., Reference Eggimann, Mutzner, Wani, Schneider, Spuhler, Moy De Vitry, Beutler and Maurer2017; Garrido-Baserba et al., Reference Garrido-Baserba, Corominas, Cortés, Rosso and Poch2020; Fu et al., Reference Fu, Jin, Sun, Yuan and Butler2022; Garzón et al., Reference Garzón, Kapelan, Langeveld and Taormina2022). To date, the AI domain of reasoning has not been as popular as the other fields in water application. However, its application is emerging due to the need for explicit reasoning, causality and explainability in AI water applications. It should be noted that the AI sub-domains are related and not disjoint (Samoili et al., Reference Samoili, Cobo, Gómez, De Prato, Martínez-Plumed and Delipetrev2020), consequently their applications to UWI systems are intertwined. For example, water distribution system design could use knowledge presentation to embed design rules in the optimisation process and integrate machine learning as a surrogate model to improve optimisation efficiency.

Table 1. The joint research centre AI taxonomy and relevant applications for UWI

Reliability, resilience and sustainability

The performance of UWI systems can be broadly described within three categories: reliability, resilience and sustainability, which jointly describe the short- and long-term service level under various conditions. These categories are not mutually exclusive but form a pyramidal relationship: reliability is necessary but not sufficient for resilience, and resilience is necessary but not sufficient for sustainability (Casal-Campos et al., Reference Casal-Campos, Fu, Butler and Moore2015; Butler et al., Reference Butler, Ward, Sweetapple, Astaraie-Imani, Diao, Farmani and Fu2017). With each category, a wide range of metrics are available to measure the operational performance of each type of UWI systems, and they need to meet some specified goals to be classified as reliable, resilient or sustainable. However, difficulties normally arise from identifying which system properties contribute to achieving reliability, resilience and sustainability. AI can be a key tool to understand the complexity of UWI systems and their short- and long-term performance and then provide solutions for performance and capacity enhancement. In general, all the performance categories can be improved by four types of data analytics using AI approaches, referred to as AI analytics: descriptive, diagnostic, predictive and prescriptive analytics. A mapping between performance and AI analytics is provided in Figure 1 and explained in detail below.

Figure 1. Use of four AI analytics to improve urban water infrastructure performance.

Reliability has been at the heart of water system design for centuries and is normally defined to measure the system performance under standard loading conditions or known threats (Butler et al., Reference Butler, Ward, Sweetapple, Astaraie-Imani, Diao, Farmani and Fu2017). It is generally represented as a probabilistic term to consider stochastic uncertainties in loadings. Reliability-based design and operation aim to reduce the likelihood of failure to achieve the specified level of service as far as is cost-effectively possible but do not consider what happens when failure occurs. Risk, a closely related concept to reliability, incorporates the consequences (often in monetary terms) of system failure or system vulnerability, though risk is sometimes treated as equivalent to reliability in some contexts such as water quality or water supply risks (e.g., Borgomeo et al., Reference Borgomeo, Mortazavi-Naeini, Hall, O’Sullivan and Watson2016).

Resilience, a concept originally emerged from ecology in the 1970s, has long been applied to water system management (e.g., Hashimoto et al., Reference Hashimoto, Stedinger and Loucks1982). There are many definitions of water system resilience (Juan-García et al., Reference Juan-García, Butler, Comas, Darch, Sweetapple, Thornton and Corominas2017), but most emphasise the ability to cope with and recover from unexpected, disruptive events. In operation, resilience is normally measured by failure duration, failure magnitude, time to failure, speed of recovery or their combinations, so AI-based identification and characterisation of failures is crucial for understanding failure patterns and developing solutions to improve UWI resilience.

Sustainability measures the performance of UWI systems in economic, environmental and social dimensions (Vinuesa et al., Reference Vinuesa, Azizpour, Leite, Balaam, Dignum, Domisch, Felländer, Langhans, Tegmark and Fuso Nerini2020). A vast number of indicators are used for each dimension, for example: using capital and operational costs, life cycle costs, and energy consumption for the economic dimension; using greenhouse gas (GHG) emissions, water quality, and ecosystem services for the environmental dimension; and using equity, equality, affordability, and public health for the social dimension. From a wider perspective, Vinuesa et al. (Reference Vinuesa, Azizpour, Leite, Balaam, Dignum, Domisch, Felländer, Langhans, Tegmark and Fuso Nerini2020) has shown that AI can have a positive impact on all eight targets for SDG6 – clean water and sanitation though it may have a negative impact on five targets.

The concepts of reliability, resilience and sustainability can be examined from two aspects: operational performance and system property. The performance aspect defines what is expected from the system in terms of service but does not describe what properties are required to deliver the performance (Butler et al., Reference Butler, Ward, Sweetapple, Astaraie-Imani, Diao, Farmani and Fu2017). System performance may arise from a number of system properties, but any one property does not guarantee a certain level of performance. For example, resilient water distribution systems normally have the following properties: robustness, flexibility, connectivity, redundancy, rapidity and resourcefulness. However, increasing connectivity does not necessarily lead to enhanced resilience because highly connected nodes may increase cascading effects of some specific failures. Further, a certain set of system properties can be related to more than one category of performance.

A wide range of interventions are available to improve reliability, resilience and sustainability of UWI systems. For example, decentralised treatment, green infrastructure (GI) and SCADA are adopted in UWI systems around the world. The interventions can be broadly organised in five development pathways: decentralisation, greening, circular economy, decarbonisation and automation. Section 3 provides a description of these pathways and how they can be enhanced by AI technologies.

Descriptive analytics

Descriptive analytics concern the use of real time or historical data to answer the question ‘what is happening’ or ‘what has happened’. This could be related to the operational states of UWI systems (e.g., water quality, flow, pressure and/or depth), key components (e.g., valves and pumps), or asset condition (e.g., structural deterioration and defect grade). These analytics provide an improved understanding of system characteristics, historical trends, operational performance and infrastructure conditions, thus can be used to develop monitoring strategies, intervention measures, benchmark standards and regulatory policies for reliability enhancement. For example, analysis of influent and effluent data from a large number of WWTPs provides an insight into treatment efficiency, energy efficiency and eco-efficiency and so provides a basis for system design benchmarking (Dong et al., Reference Dong, Zhang and Zeng2017; Longo et al., Reference Longo, Hospido, Lema and Mauricio-Iglesias2018).

Descriptive analytics can improve our knowledge on the spatio-temporal variability of external drivers to water systems and interdependencies with other systems, and thus help characterise uncertainties related to system design and operation. For example, numerous AI approaches have been used to investigate the key environmental, demographic and economic factors affecting water demand (Guo et al., Reference Guo, Liu, Wu, Li, Zhou and Zhu2018; Lee and Derrible, Reference Lee and Derrible2020; Smolak et al., Reference Smolak, Kasieczka, Fialkiewicz, Rohm, Siła-Nowicka and Kopańczyk2020; Zounemat-Kermani et al., Reference Zounemat-Kermani, Matta, Cominola, Xia, Zhang, Liang and Hinkelmann2020), aiming to support decisions on the design and operation of water distribution systems and improve hydraulic system reliability. Machine learning has been applied to generate high-resolution precipitation nowcasts by effectively capturing spatio-temporal correlations (Chen et al., Reference Chen, Cao, Ma and Zhang2020), which can potentially be applied to reduce the occurrence of urban flooding or combined sewer overflows (CSOs). Similarly, wastewater flow in sewer systems can be characterised using catchment and climate variables (Kerkez et al., Reference Kerkez, Gruden, Lewis, Montestruque, Quigley, Wong, Bedig, Kertesz, Braun, Cadwalader, Poresky and Pak2016; Lund et al., Reference Lund, Falk, Borup, Madsen and Steen Mikkelsen2018; Zhang et al., Reference Zhang, Li, Snowling, Siam and El-Dakhakhni2019) to improve operational reliability of WWTPs.

Diagnostic analytics

Diagnostic analytics are the examination of data to answer the question ‘why is it happening’ or ‘why did it happen’. It can be used to tackle failure events related to key UWI components such as water mains, sewers, CSOs, pumps, valves, aerators and sensors. New knowledge on causal relationships and failure patterns derived from diagnostic analytics can help enhance system reliability through improved design and operation. Further, system resilience can be enhanced predominantly through rapid and accurate identification of failure events to reduce their social-environmental impacts.

In water distribution systems, the deployment of online leakage detection and decision support tools can help pinpoint leaks (Zhou et al., Reference Zhou, Tang, Xu, Meng, Chu, Xin and Fu2019; Zaman et al., Reference Zaman, Tiwari, Gupta and Sen2020; Wang et al., Reference Wang, Guo, Liu, Wu, Xu and Smith2020b) and contamination event detection (Arad et al., Reference Arad, Housh, Perelman and Ostfeld2013), and thus reduce the impacts of failure (Romano et al., Reference Romano, Kapelan and Savić2014; Nikoloudi et al., Reference Nikoloudi, Romano, Memon and Kapelan2021) through rapid interventions even before water services are affected. Machine learning can identify key factors of pipe failure related to infrastructure, operation and environmental factors, and thus help develop strategies for predictive maintenance (Barton et al., Reference Barton, Hallett and Jude2022). Machine learning can significantly improve leak localisation accuracy, even with a small amount of newly monitored data when implemented real-time (Zhou et al., Reference Zhou, Tang, Xu, Meng, Chu, Xin and Fu2019). Most importantly, machine learning is the predominating approach to solve the leakage detection problem as other approaches such as mechanism models are limited due to lack of understanding of pipe deterioration mechanisms.

Similar problems in the sewer system include blockage detection and localisation (Ugarelli et al., Reference Ugarelli, Venkatesh, Brattebø, Di Federico and Sægrov2010; Okwori et al., Reference Okwori, Viklander and Hedström2021), CSO analysis and source apportionment of water pollution (Huang et al., Reference Huang, Wang, Lou, Zhou and Wu2010; Chen et al., Reference Chen, Qin, Zheng and Fu2019), and infiltration/exfiltration identification and localisation (Karpf and Krebs, Reference Karpf and Krebs2011; Guérineau et al., Reference Guérineau, Dorner, Carrière, McQuaid, Sauvé, Aboulfadl, Hajj-Mohamad and Prévost2014). Diagnostic analytics can be used to identify sensor failures such as sensor reading drift using long-term continuous monitoring (Wang et al., Reference Wang, Fan, Huang, Ling, Klimowicz, Pagano and Li2020a). In wastewater treatment processes, system faults and condition changes can be detected using statistical process control-based methods considering single or multiple variables (Newhart et al., Reference Newhart, Holloway, Hering and Cath2019).

A holistic understanding of cause-effect relationships concerning failure events is useful for UWI design and retrofit processes as resilience-enhancing properties derived by data analytics can be incorporated. For example, the interplay between six key topological attributes (i.e., connectivity, efficiency, centrality, diversity, robustness and modularity) and six resilience metrics related to system resistance, absorption and restoration capacities can guide the re-design of water distribution systems to make them more resilient (Meng et al., Reference Meng, Fu, Farmani, Sweetapple and Butler2018).

Predictive analytics

Predictive analytics are the use of real time or historical data to answer the question ‘what will or is likely to happen’. In addition to physics-based models, a wide range of data-driven approaches have been reported to predict future states, performances, events and asset conditions in UWI systems. One key aspect of sustainability involves the use of predictive analytics to assess the impacts of interventions and operations, because sustainability concerns the long-term performance of water systems, in some situations, beyond their design life. Predictive analytics can be used to estimate when key components of the system are likely to fail and thus plan maintenance work accordingly to save costly repairs or reduce extended downtime periods, which is referred to as predictive maintenance. One example of predictive maintenance is pipe deterioration prediction using AI approaches for pipe condition assessment in support of maintenance investment decisions (Berardi et al., Reference Berardi, Giustolisi, Kapelan and Savic2008; Scheidegger et al., Reference Scheidegger, Leitão and Scholten2015).

The improvement of system performance can be materialised through design and retrofit solutions, control strategies, operational actions, emergency plans and long-term adaption strategies generated from prescriptive analytics, which is normally built on the insight and knowledge gained from the other types of analytics. It is important to stress that reliability, resilience and sustainability are interlinked, the three types of data analytics, that is, descriptive, diagnostic and predictive, can provide new knowledge on the system which is then used by prescriptive analytics for actions.

Prescriptive analytics

Prescriptive analytics answers the question ‘how to operate or manage’, normally based on causal relationships and predicted outcomes using the other AI analytics. It can be used to recommend optimal operation and control strategies, real-time scheduling, and design and retrofit solutions, intervention measures and long-term management strategies in the life cycle of UWI systems. This type of analytics often refers to optimisation-based approaches. Evolutionary algorithms have become a flexible, powerful and well-used tool in solving complex water problems and applied to provide optimal operation and management options for UWI systems (Nicklow et al., Reference Nicklow, Reed, Savic, Dessalegne, Harrell, Chan-Hilton, Karamouz, Minsker, Ostfeld, Singh and Zechman2010; Maier et al., Reference Maier, Kapelan, Kasprzyk, Kollat, Matott, Cunha, Dandy, Gibbs, Keedwell, Marchi, Ostfeld, Savic, Solomatine, Vrugt, Zecchin, Minsker and Barbour2014). Though most machine-learning algorithms are generally used to gain insights from data and are not suitable for solving optimisation problems, they can be used as surrogate models in the optimisation process to improve search efficiency (Garzón et al., Reference Garzón, Kapelan, Langeveld and Taormina2022). However, reinforcement learning, a nascent type of machine learning, is able to solve sequential planning and operation problems and has been used to develop control strategies for urban flood and WWTP operation problems (Fu et al., Reference Fu, Jin, Sun, Yuan and Butler2022).

It should be noted that the four types of analytics are closely linked and sometimes a combination of different types are used to solve a practical water problem. For example, in addressing leakage and contamination detection problems, descriptive and predictive analytics can be used to understand the historical system behaviour and predict the system state respectively, and then the residuals between predicted and observed state variables are used to identify anomalies through comparison with the system variability under historical normal conditions (Arad et al., Reference Arad, Housh, Perelman and Ostfeld2013; Wang et al., Reference Wang, Guo, Liu, Wu, Xu and Smith2020b). When developing operational actions using prescriptive analytics, predictive analytics is used to estimate future system states so actions can be developed considering expected outcomes.

Moving from descriptive to prescriptive analytics increases the autonomy and intelligence of UWI systems while increasing the difficulty in the development of algorithms. All four types transform data into information, insight and knowledge, but only prescriptive analytics is able to make ‘decisions’ by generating new solutions, actions and interventions, thus moving from dumb interventions to near-optimal interventions. With the advance of wireless sensors, universal connectivity, high-speed data analytics and AI technologies, the possibility of transforming existing UWI systems into autonomous systems becomes increasingly realistic. With an autonomous water system, the degree of human intervention is low and the system is capable of performing a series of optimal operations in response to real-time, dynamic environments that are monitored and measured within the system itself.

How can AI shape the future of urban water infrastructure?

Five key characteristics of future UWI are envisioned as decentralised, green, circular, carbon neutral, and autonomous, based on the gradual evolution of water systems through interventions implemented in the last three decades. The development pathways to these characteristics are not mutually exclusive but interconnected in terms of enhancing system performance, capacity and efficiency, which ultimately contribute to resilient and sustainable water systems. For example, although adoption of swales for stormwater management is an approach to the greening pathway, it could be part of decarbonisation and decentralisation pathways as it can reduce energy consumption and GHG emissions and de-connect stormwater services from centralised sewer systems. AI technology could be incorporated in the planning, design, operation and management processes of UWI systems, as discussed in Section 2; thus, it underpins all the five development pathways: decentralisation, circular economy, decarbonisation, greening, and automation (Figure 2).

Figure 2. Five pathways towards more reliable, sustainable and resilient urban water infrastructure underpinned by artificial intelligence.

Decentralisation pathway

AI can play a key role in planning and management of decentralised systems where local facilities are optimised for water supply, stormwater management, water recycling and wastewater treatment to avoid unnecessary loss of resources (i.e., water, energy and materials). Compared to centralised systems, optimal planning of decentralised systems is a more complex problem as they should be designed to link individual decentralised systems into a system of systems that functions as a whole to achieve the required water and wastewater services and maximum environmental and ecological benefits. On transitioning to the future system, the degree of decentralisation is a key design factor for integrating decentralised systems into the existing UWI configuration and it could be optimised with prescriptive analytics such as evolutionary algorithms, considering economies of scale, topographical structure, technological advances and operational efficiency (Eggimann et al., Reference Eggimann, Truffer and Maurer2015).

Decentralisation is primarily driven by technological advances in on-site water and wastewater treatment and recycling. Garrido-Baserba et al. (Reference Garrido-Baserba, Barnosell, Molinos-Senante, Sedlak, Rabaey, Schraa, Verdaguer, Rosso and Poch2022) suggested that existing technologies can be used to create economically viable decentralised systems that eliminate the need for centralised water supply or sewage collection under some conditions. However, AI technologies are required to maximise multiple benefits of individual decentralised systems through identification of reliable and resilient operations and development of predictive maintenance strategies. In particular, AI could be used to facilitate surveys that are designed to understand public perceptions of decentralised systems by identifying participants, targeting a certain group of people and analysing collected data, and it has been increasingly used in citizen science projects for better engagement and task allocation (Ponti and Seredko, Reference Ponti and Seredko2022). This could help develop climate-resilient solutions for wider-adoption.

Circular economy pathway

WWTPs are at the heart of the circular economy approach as they are not only energy-intensive accounting for 25% of the total energy use in the water sector, but also central for water reuse, renewable energy generation and nutrient recovery with a range of technologies available (Rani et al., Reference Rani, Snyder, Kim, Lei and Pan2022). Process-based models have been used for optimising energy and nutrient recovery from wastewater treatment processes (Nakkasunchi et al., Reference Nakkasunchi, Hewitt, Zoppi and Brandoni2021). In response to a particular real-world challenge in highly variable wastewater streams, real-time monitoring of critical process parameters and nutrient attributes is increasingly implemented. This allows an integration of machine learning for accurate system dynamics simulation, enabling online learning and real-time control for maximum resources recovery.

Integration of water supply, stormwater, and wastewater systems is critical in re-shaping the flows of water, energy and materials in a UWI system to maximise reuse, recycling and recovery of resources where possible given dynamic demands and disturbances. Grey water is increasingly used for potable and non-potable water supplies, however, AI could play a key role in real-time monitoring and detection of any changes in water quality due to pathogens or chemical pollutants and facilitate rapid and appropriate responses to alleviating public health concerns and widening the adoption in communities.

The complex interrelations between various components in the UWI system provides the potential of building a water-energy-materials nexus to boost the adoption of the circular economy approach in urban water management (Fu and Butler, Reference Fu, Butler, Wang and Fu2021). AI approaches could predict future demands in water and energy and optimise resource efficiency across the entire system where individual components are operated jointly to common goals. For example, a large increase in intermittent renewable energy sources could be integrated seamlessly with the operation of energy-intensive water reuse facilities to achieve energy positive while ensuring stable and reliable operation.

Greening pathway

The greening development pathway practised in the water sector through the concept of urban GI represents a nature-based approach to stormwater and flood management. It is now widely accepted as part of UWI systems and implemented with various measures (e.g., green roofs, swales, bio-retention ponds) to achieve a wide range of benefits in water security, flood management, urban pollution, ecosystem services, carbon reduction, public health and well-being in different cities (Oral et al., Reference Oral, Carvalho, Gajewska, Ursino, Masi, Hullebusch, Kazak, Exposito, Cipolletta, Andersen, Finger, Simperler, Regelsberger, Rous, Radinja, Buttiglieri, Krzeminski, Rizzo, Dehghanian, Nikolova and Zimmermann2020). GI planning will benefit from spatial data analytics to provide insights in their impacts on system resilience, flood mitigation, and water security, ensuring GI an integral part of UWI systems as a major challenge in GI application is its design as single entities (Kerkez et al., Reference Kerkez, Gruden, Lewis, Montestruque, Quigley, Wong, Bedig, Kertesz, Braun, Cadwalader, Poresky and Pak2016).

A key challenge in promoting GI is the significant functional impairment in practice due to inappropriate operation and lack of maintenance over time. In-situ performance metrics of GI can be provided by AI tools based on continuous monitoring of water flow, water level, soil-moisture, and water quality. This information can be further fed into real-time control of stormwater systems and decision-making of retrofitting and predictive maintenance. Rainwater harvesting systems (e.g., water butts) can be operated to reduce flood risk based on rainfall forecasts provided by machine learning, with positive community engagement to emptying water before predicted rainfall events.

Sensor networks deployed for various purposes (e.g., water quality, air quality, temperature, sound and light) in a smart city should be integrated to expand our understanding of spatio-temporal ecosystem services provided by GI and thus identify prioritised interventions. Biotic and anthropogenic acoustic activity, predicted by deep learning from audio recordings provides new understanding of urban soundscapes and facilitate investigation of the impact of GI on wildlife (Fairbrass et al., Reference Fairbrass, Firman, Williams, Brostow, Titheridge and Jones2019). Urban heat island effects can be reduced by effective planning of green roofs while tackling stormwater and urban runoff pollution problems. The growing evidence on multiple benefits of GI can further stimulate the desire for GI in lieu of conventional grey infrastructure (Oral et al., Reference Oral, Carvalho, Gajewska, Ursino, Masi, Hullebusch, Kazak, Exposito, Cipolletta, Andersen, Finger, Simperler, Regelsberger, Rous, Radinja, Buttiglieri, Krzeminski, Rizzo, Dehghanian, Nikolova and Zimmermann2020).

Decarbonisation pathway

Recent studies have highlighted the importance of GHG emissions from water-related activities and the vital role of the water sector in climate change mitigation (Rothausen and Conway, Reference Rothausen and Conway2011; Rani et al., Reference Rani, Snyder, Kim, Lei and Pan2022). Energy consumption and wastewater treatment are major sources of GHG emissions in the water sector. Although new technologies have been deployed to increase renewables generation, increase energy efficiency and reduce emissions from wastewater treatment with an aim to achieving net zero targets in the water sector, the role of AI in achieving net zero emissions is increasingly recognised, as shown by the UK’s AI roadmap (UK AI COUNCIL, 2021).

Monitoring of GHG emissions in the UWI is a challenge facing the water sector, mainly due to highly complex and site-specific production processes of nitrous oxide and methane emissions and high costs of sensors. Machine learning has already shown promise in designing monitoring schemes and estimating GHG emissions in WWTPs, which help develop monitoring guidelines (Ye et al., Reference Ye, Porro and Nopens2022). A machine-learning model trained with full-scale data can be used as soft sensors to provide continuous GHG emissions data. This is valuable in providing insights into GHG emissions variability or production processes by integrating soft sensors and mechanistic models (Li et al., Reference Li, Duan, Liu, Qiu, van den Akker, Ni, Chen, Yin, Yuan and Ye2022b).

Optimal control empowered by AI can reduce both direct and indirect GHG emissions in the UWI system. WWTPs are highly energy-dependent, so control strategies could be developed using a range of AI methods to balance the GHG emissions and effluent water quality (Sweetapple et al., Reference Sweetapple, Fu and Butler2014), though a positive correlation between nitrous oxide emissions and total nitrogen is commonly accepted (Duan et al., Reference Duan, van den Akker, Thwaites, Peng, Herman, Pan, Ni, Watt, Yuan and Ye2020). Pump scheduling in water distribution and wastewater systems should consider future demand or flow predictions, intermittence of on-site renewables and varying prices of the grid energy. Aeration pumping can be optimised to make use of varying dilution capacity in the receiving water while meeting water quality standards (Meng et al., Reference Meng, Fu and Butler2017).

Automation pathway

Automation is widely utilised in water and WWTPs due to advances in sensing, communication and computing technologies, however, it is mainly limited to control of individual process units or several units in a system (Yuan et al., Reference Yuan, Olsson, Cardell-Oliver, van Schagen, Marchi, Deletic, Urich, Rauch, Liu and Jiang2019). Research on integrated control of UWI systems has progressed rapidly over the past decades (Fu et al., Reference Fu, Butler and Khu2008), however real-world applications are limited. Challenges in improving automation or building fully autonomous water systems are profound from many aspects: complex interactions between different system components, uncertainties in future predictions, explainability of control strategies and AI trustworthiness, capital investments required for monitoring and software.

Machine learning can be integrated into system control methods for improved control performance. Significantly improved water quality, system reliability and energy efficiency are amongst the benefits reported through AI integration, for example, the use of forecasted demands to control the outflow from water treatment plants (Bakker et al., Reference Bakker, Vreeburg, Palmen, Sperber, Bakker and Rietveld2013) and the use of rainfall and flow forecasts to control CSOs and wastewater treatment processes (Lund et al., Reference Lund, Borup, Madsen, Mark, Arnbjerg-Nielsen and Mikkelsen2019). The latest deep learning technology has greatly improved the forecasting accuracy in water demand, pressure, flow, water depth and pollution load (Wang et al., Reference Wang, Man, Hu, Li, Hong and Cui2019), thus is promising in improving system control.

Deep reinforcement learning has great promise of tackling the problems in current control algorithms such as highly uncertain disturbances and intensive computing times. It is anticipated that research in deep reinforcement learning in the next decades will enable more automated control of the UWI system or the incorporation of some autonomous components into physical infrastructure systems.

AI attributes to support development pathways

AI has many attributes that distinguish it from other technologies. The following key attributes are well suited to support the development pathways identified and should be considered when designing an AI system to solve water management problems.

  1. 1. Adaptability. AI systems can adapt to changing conditions and environments and improve their performance over time without explicit programming. This is mainly achieved through machine learning to allow self-learning from data and experience. This attribute is useful for accurate representation of UWI systems, which often change in response to urbanisation and climate change through engineering intervention.

  2. 2. Autonomy: AI systems can be designed to operate independently with no or low level of direct human supervision. Many repetitive tasks in the management of UWI systems could be potentially automated at relatively low-cost (Garrido-Baserba et al., Reference Garrido-Baserba, Corominas, Cortés, Rosso and Poch2020). One example is sewer defect detection through computer vision technologies to process large amounts of CCTV images obtained by water companies (Myrans et al., Reference Myrans, Everson and Kapelan2018).

  3. 3. Scalability: AI systems can be easily scaled up or down to meet the needs of different water systems and data availability. They can be developed and deployed for a component, decentralised system at household and community levels, or large-scale system at the city and catchment levels. In particular, they are capable to handle large amounts of data, making it suitable for large-scale systems.

  4. 4. Parallellisation: AI systems can make use of parallel computing resources and distributed data for efficient calculation and effective communication. They could be used for integrated control of a water system, where the operation of individual controllers is based on independently trained AI systems to capture local conditions but co-ordinated across the system to achieve high-level system objectives. For example, multiple agents have been developed to optimise DO and dosage simultaneously in wastewater treatment processes (Chen et al., Reference Chen, Wang, Valverde-P’erez, Zhai, Vezzaro and Wang2021).

  5. 5. Efficiency: AI systems can be computationally efficient in handling large amounts of data and large-scale systems. Though many machine-learning algorithms could be time-consuming during training, they are extremely efficient in implementation after training. Further recent advances have been made in data-centric approaches which explore training with small data sets (Liu et al., Reference Liu, Savic and Fu2023), and transfer learning which allow algorithms to perform different tasks which they are not trained for. This makes AI systems suitable as a surrogate of hydraulic models for computationally intensive tasks such as optimal system design, real-time control, and uncertainty analysis (Garzón et al., Reference Garzón, Kapelan, Langeveld and Taormina2022).

The AI attributes have been translated into advantages as shown by case studies in the literature (Fu et al., Reference Fu, Jin, Sun, Yuan and Butler2022). Examples include processing high spatio-temporal resolution data for demand prediction (Zounemat-Kermani et al., Reference Zounemat-Kermani, Matta, Cominola, Xia, Zhang, Liang and Hinkelmann2020), considering correlations of multi-variate time series for more accurate contamination detection (Li et al., Reference Li, Liu, Zhang and Fu2023), high efficiency and accuracy in video processing (Myrans et al., Reference Myrans, Everson and Kapelan2018), and robust control in an uncertain environment (Xu et al., Reference Xu, Meng, Guo, Li and Fu2021b).

Practical implications and barriers in AI application

Although the transformative potential of AI in UWI becomes clear in enhancing performance, capacity and efficiency, we must recognise a number of practical implications and barriers may that limit its wide adoption in the water sector to support the five pathways described. The implication and barriers can be categorised in terms of four dimensions: cyber-physical infrastructure and institutional governance in the water sector, and social-economic and technological development in wider society, as shown in Figure 3.

Figure 3. Practical implications and barriers for AI adoption in the water sector.

Public sector water utilities generally lack a clear strategy for digital transformation and organisational culture for changes in technology and operations as they do not face competitive market pressures, nor do they have the option of rapidly developing new business models (Boyle et al., Reference Boyle, Ryan, Bhandari, Pratik, KMY, Gong and Creighton2022). This leads to low investments for development of digital skills in the water sector. A healthy AI ecosystem involving water utilities, IT companies, consultancies and academia is needed to speed up the adoption of AI tools for water management (Garrido-Baserba et al., Reference Garrido-Baserba, Corominas, Cortés, Rosso and Poch2020).

Given the complexity of UWI systems, difficulties remain in identifying AI applications which can make a breakthrough in fundamentally transforming water system operation and management, though a few areas such sewer defect and leakage detection are emerging (Fu et al., Reference Fu, Jin, Sun, Yuan and Butler2022). Development of tailor-made AI models based on the latest deep learning algorithms might improve the availability and maturity of AI technology in the water sector. Availability of large data sets should be tackled when identifying and developing AI tools. Improving explainability is also key for users to understand predictions and decisions from AI tools and thus encourage their adoption in the water sector.

Though the advance in information and communication technologies has enabled the proliferation of sensors in UWI systems, there is still a significant gap in system monitoring considering the large number of variables and distributed components that need monitoring. Research communities continue to develop low cost and high reliability sensors required for understanding real-time system dynamics. Significant capital investment is needed for data infrastructure, AI platforms and tools that can store and process the unprecedented amount of data being collected.

When AI becomes embedded in many processes, services and products in the water sector, it will have a profound impact on society from many aspects: data privacy, ethical and legal concerns, risks and unintended consequences from adoption of AI-based systems and their failure (de Vitry et al., Reference de Vitry, Schneider, Wani, Manny, Leitao and Eggimann2019). Some fear that automation driven by AI could lead to job losses. Incorporating AI to support the pathways needs to reflect its speed and scope of adoption, so appropriate regulation and governance is needed to enable accountability, trustworthiness and transparency to ensure social and economic benefits from AI research and development.

Conclusions

This review sought to analyse and discuss how AI might shape the future development of UWI systems. The four types of AI analytics, descriptive, diagnostic, predictive and prescriptive, are found to contribute to improving system performance based on three categories, that is, reliability, resilience and sustainability. We envision a future where AI will support the development of five pathways towards UWI systems of the future: decentralisation, circular economy, greening, decarbonisation and automation. This shows profound opportunities of AI application for the water sector in terms of how interventions should be developed and incorporated into the existing infrastructure system using AI-based methods and tools. The barriers and challenges in AI adoption for enhancing the development of pathways are characterised on the basis of four dimensions: cyber-physical infrastructure, institutional governance, social-economic systems and technological development in the water sector and wider society.

We advocate a pivotal role of AI technologies in moving towards reliable, resilient and sustainable UWI systems. Given the breadth and significance of potential AI applications, the water sector needs to significantly increase capital investments on AI systems and skills, building on the investments already made to SCADA and digitalisation in the last three decades. Developing an interdisciplinary and interactive approach to tackling the barriers is essential to ensure that AI-based systems are developed and deployed in a responsible way to build the future UWI systems.

The synthesis of the role of AI was focused on the cyber-physical component of UWI in this review. In addition, AI could support the social-economic aspects of UWI, such as public engagement, public perception, human–infrastructure interactions, citizen science and customer service, which should be further analysed in the future.

Open peer review

To view the open peer review materials for this article, please visit http://doi.org/10.1017/wat.2023.15.

Data availability statement

Data sharing are not applicable to this article as no datasets were generated during the current study.

Author contribution

All authors contributed to the conceptualisation and development of this manuscript. G.F. wrote the initial draft and all authors reviewed, edited and approved the final manuscript.

Financial support

This work was supported by the Royal Society under the Industry fellowship scheme (grant number IF160108); the Alan Turing Institute under the EPSRC grant (grant number EP/N510129/1); and the National Natural Science Foundation of China (grant number 42071272).

Competing interest

There are no financial or nonfinancial interests to disclose by the authors.

References

Arad, J, Housh, M, Perelman, L and Ostfeld, A (2013) A dynamic thresholds scheme for contaminant event detection in water distribution systems. Water Research 47, 18991908. https://doi.org/10.1016/j.watres.2013.01.017.CrossRefGoogle ScholarPubMed
Bakker, M, Vreeburg, JHG, Palmen, LJ, Sperber, V, Bakker, G and Rietveld, LC (2013) Better water quality and higher energy efficiency by using model predictive flow control at water supply systems. Journal of Water Supply: Research and Technology - AQUA 62, 113. https://doi.org/10.2166/aqua.2013.063.CrossRefGoogle Scholar
Barton, NA, Hallett, SH and Jude, SR (2022) Predicting the risk of pipe failure using gradient boosted decision trees and weighted risk analysis. npj Clean Water 5, 22. https://doi.org/10.1038/s41545-022-00165-2.CrossRefGoogle Scholar
Berardi, L, Giustolisi, O, Kapelan, Z and Savic, DA (2008) Development of pipe deterioration models for water distribution systems using EPR. Journal of Hydroinformatics 10, 113126. https://doi.org/10.2166/hydro.2008.012.CrossRefGoogle Scholar
Bhola, PK, Nair, BB, Leandro, J, Rao, SN and Disse, M (2019) Flood inundation forecasts using validation data generated with the assistance of computer vision. Journal of Hydroinformatics 21(2), 240256.CrossRefGoogle Scholar
Borgomeo, E, Mortazavi-Naeini, M, Hall, JW, O’Sullivan, MJ and Watson, T (2016) Trading-off tolerable risk with climate change adaptation costs in water supply systems. Water Resources Research 52, 622643. https://doi.org/10.1002/2015WR018164CrossRefGoogle Scholar
Boyle, C, Ryan, G, Bhandari, , Pratik, , KMY, Law, Gong, J and Creighton, D (2022) Digital transformation in water organizations. Journal of Water Resources Planning and Management 148(7) 03122001. https://doi.org/10.1061/(ASCE)WR.1943-5452.0001555.CrossRefGoogle Scholar
Brown, RR, Keath, N and Wong, THF (2009) Urban water management in cities: Historical, current and future regimes. Water Science and Technology 59, 847855. https://doi.org/10.2166/wst.2009.029.CrossRefGoogle ScholarPubMed
Butler, D, Ward, S, Sweetapple, C, Astaraie-Imani, M, Diao, K, Farmani, R and Fu, G (2017) Reliable, resilient and sustainable water management: The safe & SuRe approach. Global Challenges 1, 6377. https://doi.org/10.1002/gch2.1010.CrossRefGoogle ScholarPubMed
Casal-Campos, A, Fu, G, Butler, D and Moore, A (2015 ) An integrated environmental assessment of green and gray infrastructure strategies for robust decision making. Environmental Science & Technology 49, 83078314. https://doi.org/10.1021/es506144f.CrossRefGoogle ScholarPubMed
Chen, L, Cao, Y, Ma, L and Zhang, J (2020) A deep learning-based methodology for precipitation Nowcasting with radar. Earth and Space Science 7, e2019EA000812. https://doi.org/10.1029/2019EA000812.CrossRefGoogle Scholar
Chen, S, Qin, H-p, Zheng, Y and Fu, G (2019) Spatial variations of pollutants from sewer interception system overflow. Journal of Environmental Management 233, 748756. https://doi.org/10.1016/j.jenvman.2018.09.082.CrossRefGoogle ScholarPubMed
Chen, K, Wang, H, Valverde-P’erez, B, Zhai, S, Vezzaro, L and Wang, A (2021) Optimal control towards sustainable wastewater treatment plants based on multi-agent reinforcement learning. Chemosphere 279, 130498. https://doi.org/10.1016/j.chemosphere.2021.130498.CrossRefGoogle ScholarPubMed
Chau, K and Cheung, CS (2004) Knowledge representation on design of storm drainage system. In Orchard, B, Yang, C and Ali, M (eds), International Conference on Industrial, Engineering and Other Applications of Applied Intelligent Systems. Berlin–Heidelberg: Springer, pp. 886894.Google Scholar
Daniel, I, Ajami, NK, Castelletti, A, Savic, D, Stewart, RA and Cominola, A (2023) A survey of water utilities’ digital transformation: Drivers, impacts, and enabling technologies. npj Clean Water 6, 51. https://doi.org/10.1038/s41545-023-00265-7.CrossRefGoogle Scholar
de Vitry, MM, Schneider, MY, Wani, O, Manny, L, Leitao, JP and Eggimann, S (2019) Smart urban water systems: What could possibly go wrong? Environmental Research Letters 14, 081001. https://doi.org/10.1088/1748-9326/ab3761.CrossRefGoogle Scholar
Dong, X, Zhang, X and Zeng, S (2017) Measuring and explaining eco-efficiencies of wastewater treatment plants in China: An uncertainty analysis perspective. Water Research 112, 195207. https://doi.org/10.1016/j.watres.2017.01.026.CrossRefGoogle Scholar
Duan, H, van den Akker, B, Thwaites, BJ, Peng, L, Herman, C, Pan, Y, Ni, BJ, Watt, S, Yuan, Z and Ye, L (2020) Mitigating nitrous oxide emissions at a full-scale wastewater treatment plant. Water Research 185, 116196. https://doi.org/10.1016/j.watres.2020.116196.CrossRefGoogle Scholar
Eggimann, S, Mutzner, L, Wani, O, Schneider, MY, Spuhler, D, Moy De Vitry, M, Beutler, P and Maurer, M (2017) The potential of knowing more: A review of data-driven urban water management. Environmental Science & Technology 51, 25382553. https://doi.org/10.1021/acs.est.6b04267.CrossRefGoogle Scholar
Eggimann, S, Truffer, B and Maurer, M (2015) To connect or not to connect ? Modelling the optimal degree of centralisation for wastewater infrastructures. Water Research 84, 218231. https://doi.org/10.1016/j.watres.2015.07.004.CrossRefGoogle ScholarPubMed
Fairbrass, AJ, Firman, M, Williams, C, Brostow, GJ, Titheridge, H and Jones, KE (2019) CityNet—Deep learning tools for urban ecoacoustic assessment. Methods in Ecology and Evolution 10, 186197. https://doi.org/10.1111/2041-210X.13114.CrossRefGoogle Scholar
Fu, G, Butler, D and Khu, S-T (2008) Multiple objective optimal control of integrated urban wastewater systems. Environmental Modelling and Software 23, 225234. https://doi.org/10.1016/j.envsoft.2007.06.003.CrossRefGoogle Scholar
Fu, G, Khu, ST and Butler, D (2010) Optimal distribution and control of storage tank to mitigate the impact of new developments on receiving water quality. Journal of Environmental Engineering 136(3), 335342. https://doi.org/10.1061/(ASCE)EE.1943-7870.0000161.CrossRefGoogle Scholar
Fu, G, Kapelan, Z, Kasprzyk, J and Reed, P (2013) Optimal design of water distribution systems using many-objective visual analytics. Journal of Water Resources Planning and Management 139(6), 624633.CrossRefGoogle Scholar
Fu, G, Jin, Y, Sun, S, Yuan, Z and Butler, D (2022) The role of deep learning in urban water management: A critical review. Water Research 223, 118973. https://doi.org/10.1016/j.watres.2022.118973.CrossRefGoogle ScholarPubMed
Fu, G, Makropoulos, C and Butler, D (2010) Simulation of urban wastewater systems using artificial neural networks: Embedding urban areas in integrated catchment modelling. Journal of Hydroinformatics 12, 140149. https://doi.org/10.2166/hydro.2009.151.CrossRefGoogle Scholar
Fu, G and Kapelan, Z (2011) Fuzzy probabilistic design of water distribution networks. Water Resources Research 47, article no. W05538. https://doi.org/10.1029/2010WR009739.CrossRefGoogle Scholar
Fu, G, Butler, D, Khu, ST and Sun, S (2011) Imprecise probabilistic evaluation of sewer flooding in urban drainage systems using random set theory. Water Resources Research 47. https://doi.org/10.1029/2009WR008944.CrossRefGoogle Scholar
Fu, G, Butler, D (2021) Pathways towards sustainable and resilient urban water systems. In Wang, XC and Fu, G (eds), Water-Wise Cities and Sustainable Water Systems: Concepts, Technologies, and Applications. London: IWA publishing. DOI: 10.2166/9781789060768_0003.Google Scholar
Garrido-Baserba, M, Barnosell, I, Molinos-Senante, M, Sedlak, DL, Rabaey, K, Schraa, O, Verdaguer, M, Rosso, D and Poch, M (2022 ) The third route: A techno-economic evaluation of extreme water and wastewater decentralization. Water Research 218, 118408. https://doi.org/10.1016/j.watres.2022.118408.CrossRefGoogle ScholarPubMed
Garrido-Baserba, M, Corominas, L, Cortés, U, Rosso, D and Poch, M (2020) The fourth-revolution in the water sector encounters the digital revolution. Environmental Science & Technology 54, 46984705. https://doi.org/10.1021/acs.est.9b04251.CrossRefGoogle ScholarPubMed
Garzón, A, Kapelan, Z, Langeveld, J and Taormina, R (2022) Machine learning-based surrogate modelling for urban water networks: Review and future research directions. Water Resources Research 2022, e2021WR031808.CrossRefGoogle Scholar
Guérineau, H, Dorner, S, Carrière, A, McQuaid, N, Sauvé, S, Aboulfadl, K, Hajj-Mohamad, M and Prévost, M (2014) Source tracking of leaky sewers: A novel approach combining fecal indicators in water and sediments. Water Research 58, 5061. https://doi.org/10.1016/j.watres.2014.03.057.CrossRefGoogle ScholarPubMed
Guo, G, Liu, S, Wu, Y, Li, J, Zhou, R and Zhu, X (2018) Short-term water demand forecast based on deep learning method. Journal of Water Resources Planning and Management 144, 111. https://doi.org/10.1061/(ASCE)WR.1943-5452.0000992.CrossRefGoogle Scholar
Hashimoto, T, Stedinger, JR, and Loucks, DP (1982) Reliability, resiliency, and vulnerability criteria for water resource system performance evaluation. Water Resources Research 18(1), 1420.CrossRefGoogle Scholar
Huang, F, Wang, X, Lou, L, Zhou, Z and Wu, J (2010) Spatial variation and source apportionment of water pollution in Qiantang River (China) using statistical techniques. Water Research 44, 15621572. https://doi.org/10.1016/j.watres.2009.11.003.CrossRefGoogle ScholarPubMed
IWA (2019) Digital Water: Industry leaders chart the transformation journey. The International Water Association, London. https://iwa-network.org/wp-content/uploads/2019/06/IWA_2019_Digital_Water_Report.pdf.Google Scholar
Juan-García, P, Butler, D, Comas, J, Darch, G, Sweetapple, C, Thornton, A and Corominas, L (2017) Resilience theory incorporated into urban wastewater systems management. State of the art. Water Research 115, 149161. https://doi.org/10.1016/j.watres.2017.02.047.CrossRefGoogle Scholar
Karpf, C and Krebs, P (2011) Quantification of groundwater infiltration and surface water inflows in urban sewer networks based on a multiple model approach. Water Research 45, 31293136. https://doi.org/10.1016/j.watres.2011.03.022.CrossRefGoogle ScholarPubMed
Kerkez, B, Gruden, C, Lewis, M, Montestruque, L, Quigley, M, Wong, B, Bedig, A, Kertesz, R, Braun, T, Cadwalader, O, Poresky, A and Pak, C (2016) Smarter stormwater systems. Environmental Science & Technology 50, 72677273. https://doi.org/10.1021/acs.est.5b05870.CrossRefGoogle ScholarPubMed
Lee, D and Derrible, S (2020) Predicting residential water demand with machine-based statistical learning. Journal of Water Resources Planning and Management 146, 04019067. https://doi.org/10.1061/(asce)wr.1943-5452.0001119.CrossRefGoogle Scholar
Li, J, Li, W, Chang, X, Sharma, K and Yuan, Z (2022a) Real-time predictive control for chemical distribution in sewer networks using improved elephant herding optimization. IEEE Transactions on Industrial Informatics 18, 571581. https://doi.org/10.1109/TII.2020.3028429.CrossRefGoogle Scholar
Li, K, Duan, H, Liu, L, Qiu, R, van den Akker, B, Ni, BJ, Chen, T, Yin, H, Yuan, Z and Ye, L (2022b) An integrated first principal and deep learning approach for modeling nitrous oxide emissions from wastewater treatment plants. Environmental Science & Technology 56, 28162826. https://doi.org/10.1021/acs.est.1c05020.CrossRefGoogle ScholarPubMed
Li, Z, Liu, H, Zhang, C and Fu, G (2023) Generative adversarial networks for detecting contamination events in water distribution systems using multi-parameter, multi-site water quality monitoring. Environmental Science and Ecotechnology 14, 100231.CrossRefGoogle ScholarPubMed
Liu, G, Savic, D and Fu, G (2023) Short-term water demand forecasting using data-centric machine learning approaches. Journal of Hydroinformatics 25(3), 895911.CrossRefGoogle Scholar
Longo, S, Hospido, A, Lema, JM and Mauricio-Iglesias, M (2018) A systematic methodology for the robust quantification of energy efficiency at wastewater treatment plants featuring data envelopment analysis. Water Research 141, 317328. https://doi.org/10.1016/j.watres.2018.04.067.CrossRefGoogle ScholarPubMed
Lund, NSV, Borup, M, Madsen, H, Mark, O, Arnbjerg-Nielsen, K and Mikkelsen, PS (2019) Integrated stormwater inflow control for sewers and green structures in urban landscapes. Nature Sustainability 2, 10031010. https://doi.org/10.1038/s41893-019-0392-1.CrossRefGoogle Scholar
Lund, NSV, Falk, AKV, Borup, M, Madsen, H and Steen Mikkelsen, P (2018) Model predictive control of urban drainage systems: A review and perspective towards smart real-time water management. Critical Reviews in Environmental Science and Technology 48, 279339. https://doi.org/10.1080/10643389.2018.1455484.CrossRefGoogle Scholar
Maier, HR, Kapelan, Z, Kasprzyk, J, Kollat, J, Matott, LS, Cunha, MC, Dandy, GC, Gibbs, MS, Keedwell, E, Marchi, A, Ostfeld, A, Savic, D, Solomatine, DP, Vrugt, JA, Zecchin, AC, Minsker, BS and Barbour, EJ (2014) Evolutionary algorithms and other metaheuristics in water resources: Current status, research challenges and future directions. Environmental Modelling and Software 62, 271299. https://doi.org/10.1016/j.envsoft.2014.09.013.CrossRefGoogle Scholar
Meng, F, Fu, G and Butler, D (2017) Cost-effective river water quality management using integrated real-time control technology. Environmental Science & Technology 51, 98769886. https://doi.org/10.1021/acs.est.7b01727.CrossRefGoogle ScholarPubMed
Meng, F, Fu, G, Farmani, R, Sweetapple, C, Butler, D (2018 ) Topological attributes of network resilience: A study in water distribution systems. Water Research 143, 376386. https://doi.org/10.1016/j.watres.2018.06.048.CrossRefGoogle ScholarPubMed
Myrans, J, Everson, R and Kapelan, Z (2018) Automated detection of faults in sewers using CCTV image sequences. Automation in Construction 95, 6471.CrossRefGoogle Scholar
Nakkasunchi, S, Hewitt, NJ, Zoppi, C and Brandoni, C (2021) A review of energy optimization modelling tools for the decarbonisation of wastewater treatment plants. Journal of Cleaner Production 279, 123811. https://doi.org/10.1016/j.jclepro.2020.123811.CrossRefGoogle Scholar
Newhart, KB, Holloway, RW, Hering, AS and Cath, TY (2019) Data-driven performance analyses of wastewater treatment plants: A review. Water Research 157, 498513. https://doi.org/10.1016/j.watres.2019.03.030.CrossRefGoogle ScholarPubMed
Nicklow, J, Reed, P, Savic, D, Dessalegne, T, Harrell, L, Chan-Hilton, A, Karamouz, M, Minsker, B, Ostfeld, A, Singh, A and Zechman, E (2010) State of the art for genetic algorithms and beyond in water resources planning and management. Journal of Water Resources Planning and Management 136, 412432. https://doi.org/10.1061/(ASCE)WR.1943-5452.0000053.CrossRefGoogle Scholar
Nikoloudi, E, Romano, M, Memon, FA and Kapelan, Z (2021) Interactive decision support methodology for near real-time response to failure events in a water distribution network. Journal of Hydroinformatics 23, 483499. https://doi.org/10.2166/HYDRO.2020.101.CrossRefGoogle Scholar
Okwori, E, Viklander, M and Hedström, A (2021) Spatial heterogeneity assessment of factors affecting sewer pipe blockages and predictions. Water Research 194, 116934. https://doi.org/10.1016/j.watres.2021.116934.CrossRefGoogle ScholarPubMed
Oral, HV, Carvalho, P, Gajewska, M, Ursino, N, Masi, F, Hullebusch, ED v, Kazak, JK, Exposito, A, Cipolletta, G, Andersen, TR, Finger, DC, Simperler, L, Regelsberger, M, Rous, V, Radinja, M, Buttiglieri, G, Krzeminski, P, Rizzo, A, Dehghanian, K, Nikolova, M and Zimmermann, M (2020) A review of nature-based solutions for urban water management in European circular cities: A critical assessment based on case studies and literature. Blue-Green Systems 2, 112136. https://doi.org/10.2166/bgs.2020.932.CrossRefGoogle Scholar
Perelman, L and Ostfeld, A (2011) Topological clustering for water distribution systems analysis. Environmental Modelling & Software 26(7), 969972.CrossRefGoogle Scholar
Ponti, M and Seredko, A (2022) Human-machine-learning integration and task allocation in citizen science. Humanities and Social Sciences Communications 9, 48. https://doi.org/10.1057/s41599-022-01049-z.CrossRefGoogle Scholar
Rani, A, Snyder, SW, Kim, H, Lei, Z and Pan, SY (2022) Pathways to a net-zero-carbon water sector through energy-extracting wastewater technologies. npj Clean Water 5, 117. https://doi.org/10.1038/s41545-022-00197-8.CrossRefGoogle Scholar
Rapp, AH, Capener, AM and Sowby, RB (2023) Adoption of artificial intelligence in drinking water operations: A survey of Progress in the United States. Journal of Water Resources Planning and Management 149(7), 06023002.CrossRefGoogle Scholar
Richards, CE, Tzachor, A, Avin, S and Fenner, R (2023) Rewards, risks and responsible deployment of artificial intelligence in water systems. Nature Water 1, 422432.CrossRefGoogle Scholar
Rodriguez-Perez, J, Leigh, C, Liquet, B, Kermorvant, C, Peterson, E, Sous, D and Mengersen, K (2020) Detecting technical anomalies in high-frequency water-quality data using artificial neural networks. Environmental Science & Technology 54, 1371913730. https://doi.org/10.1021/acs.est.0c04069.CrossRefGoogle ScholarPubMed
Romano, M, Kapelan, Z and Savić, DA (2014) Automated detection of pipe bursts and other events in water distribution systems. Journal of Water Resources Planning and Management 140, 457467. https://doi.org/10.1061/(asce)wr.1943-5452.0000339.CrossRefGoogle Scholar
Rothausen, SGSA and Conway, D (2011) Greenhouse-gas emissions from energy use in the water sector. Nature Climate Change 1, 210219. https://doi.org/10.1038/nclimate1147.CrossRefGoogle Scholar
Samoili, S, Cobo, ML, Gómez, E, De Prato, G, Martínez-Plumed, F and Delipetrev, B (2020) AI Watch. Defining Artificial Intelligence. Towards an operational definition and taxonomy of artificial intelligence. EUR 30117 EN, Publications Office of the European Union, Luxembourg, 2020, JRC118163. https://doi.org/10.2760/382730.CrossRefGoogle Scholar
Sadr, SMK, Casal-Campos, A, Fu, G, Farmani, R, Ward, S and Butler, D (2020) Strategic planning of the integrated urban wastewater system using adaptation pathways. Water Research 182, 116013, article no. 116013. https://doi.org/10.1016/j.watres.2020.116013.CrossRefGoogle ScholarPubMed
Scheidegger, A, Leitão, JP and Scholten, L (2015) Statistical failure models for water distribution pipes: A review from a unified perspective. Water Research 83, 237247. https://doi.org/10.1016/j.watres.2015.06.027.CrossRefGoogle ScholarPubMed
Smolak, K, Kasieczka, B, Fialkiewicz, W, Rohm, W, Siła-Nowicka, K and Kopańczyk, K (2020) Applying human mobility and water consumption data for short-term water demand forecasting using classical and machine learning models. Urban Water Journal 17, 3242. https://doi.org/10.1080/1573062X.2020.1734947.CrossRefGoogle Scholar
Stewart, RA, Nguyen, K, Beal, C, Zhang, H, Sahin, O, Bertone, E, Silva-Vieira, A, Castelletti, A, Cominola, A, Giuliani, M, Giurco, D, Blumenstein, M, Turner, A, Liu, A, Kenway, S, Savic, DA, Makropoulos, C and Kossieris, P (2018) Integrated intelligent water-energy metering systems and informatics: Visioning a digital multi-utility service provider. Environmental Modelling & Software 105, 94117.CrossRefGoogle Scholar
Sweetapple, C, Fu, G and Butler, D (2014) Multi-objective optimisation of wastewater treatment plant control to reduce greenhouse gas emissions. Water Research 55, 5262. https://doi.org/10.1016/j.watres.2014.02.018.CrossRefGoogle ScholarPubMed
The Royal Society (2017) Machine learning: The power and promise of computers that learn by example. Report by the Royal Society. https://doi.org/10.1126/scitranslmed.3002564.CrossRefGoogle Scholar
Ugarelli, R, Venkatesh, G, Brattebø, H, Di Federico, V and Sægrov, S (2010) Historical analysis of blockages in wastewater pipelines in Oslo and diagnosis of causative pipeline characteristics. Urban Water Journal 7, 335343. https://doi.org/10.1080/1573062X.2010.526229.CrossRefGoogle Scholar
Vertommen, I, Tian, X, Pronk, T, Seshan, S, Paraskevopoulos, S and Wols, B (2023) Exploring the Value of Natural Language Processing for Urban Water Research, EGU General Assembly 2023, Vienna, Austria, 24–28 April 2023, EGU23–1218, 2023. https://doi.org/10.5194/egusphere-egu23-1218.CrossRefGoogle Scholar
Vinuesa, R, Azizpour, H, Leite, I, Balaam, M, Dignum, V, Domisch, S, Felländer, A, Langhans, SD, Tegmark, M and Fuso Nerini, F (2020) The role of artificial intelligence in achieving the sustainable development goals. Nature Communications 11, 110. https://doi.org/10.1038/s41467-019-14108-y.CrossRefGoogle ScholarPubMed
Wang, X, Fan, Y, Huang, Y, Ling, J, Klimowicz, A, Pagano, G and Li, B (2020a) Solving sensor reading drifting using denoising data processing algorithm (DDPA) for long-term continuous and accurate monitoring of ammonium in wastewater. ACS ES&T Water 1, 530541. https://doi.org/10.1021/acsestwater.0c00077.CrossRefGoogle Scholar
Wang, X, Guo, G, Liu, S, Wu, Y, Xu, X and Smith, K (2020b) Burst detection in district metering areas using deep learning method. Journal of Water Resources Planning and Management 146, 04020031. https://doi.org/10.1061/(asce)wr.1943-5452.0001223.CrossRefGoogle Scholar
Wang, Z, Man, Y, Hu, Y, Li, J, Hong, M and Cui, P (2019) A deep learning based dynamic COD prediction model for urban sewage. Environmental Science: Water Research & Technology 5, 22102218. https://doi.org/10.1039/c9ew00505f.Google Scholar
Wei, L, Magee, DR, Dimitrova, V, Clarke, B, Du, H, Mahesar, QA, Al Ammari, K and Cohn, AG (2018) Automated reasoning for city infrastructure maintenance decision support. In Lang, Jérôme (eds), Proceedings of the Twenty-Seventh International Joint Conference on Artificial Intelligence. International Joint Conferences on Artificial Intelligence, Stockholm, Sweden.Google Scholar
Xu, Y, Liu, X, Cao, X, Huang, C, Liu, E, Qian, S, Liu, X, Wu, Y, Dong, F, Qiu, C-W, Qiu, J, Hua, K, Su, W, Wu, J, Xu, H, Han, Y, Fu, C, Yin, Z, Liu, M, Roepman, R, Dietmann, S, Virta, M, Kengara, F, Zhang, Z, Zhang, L, Zhao, T, Dai, J, Yang, J, Lan, L, Luo, M, Liu, Z, An, T, Zhang, B, He, X, Cong, S, Liu, X, Zhang, W, Lewis, JP, Tiedje, JM, Wang, Q, An, Z, Wang, F, Zhang, L, Huang, T, Lu, C, Cai, Z, Wang, F and Zhang, J (2021a) Artificial intelligence: A powerful paradigm for scientific research. Innovations 2, 100179.Google ScholarPubMed
Xu, W, Meng, F, Guo, W, Li, X and Fu, G (2021b) Deep reinforcement learning for optimal hydropower reservoir operation. Journal of Water Resources Planning and Management 147(8), 04021045. https://doi.org/10.1061/(ASCE)WR.1943-5452.0001409.CrossRefGoogle Scholar
Ye, L, Porro, J and Nopens, I (2022) Quantification and Modelling of Fugitive Greenhouse Gas Emissions from Urban Water Systems. IWA publishing, London. https://doi.org/10.2166/9781789060461.CrossRefGoogle Scholar
Yu, F, Li, XY and Han, XS (2018) Risk response for urban water supply network using case-based reasoning during a natural disaster. Safety Science 106, 121139.CrossRefGoogle Scholar
Yuan, Z, Olsson, G, Cardell-Oliver, R, van Schagen, K, Marchi, A, Deletic, A, Urich, C, Rauch, W, Liu, Y and Jiang, G (2019) Sweating the assets – The role of instrumentation, control and automation in urban water systems. Water Research 155, 381402. https://doi.org/10.1016/j.watres.2019.02.034.CrossRefGoogle ScholarPubMed
Zaman, D, Tiwari, MK, Gupta, AK and Sen, D (2020) A review of leakage detection strategies for pressurised pipeline in steady-state. Engineering Failure Analysis 109, 104264. https://doi.org/10.1016/j.engfailanal.2019.104264.CrossRefGoogle Scholar
Zhang, Q, Li, Z, Snowling, S, Siam, A and El-Dakhakhni, W (2019) Predictive models for wastewater flow forecasting based on time series analysis and artificial neural network. Water Science and Technology 80, 243253. https://doi.org/10.2166/wst.2019.263.CrossRefGoogle ScholarPubMed
Zhou, X, Tang, Z, Xu, W, Meng, F, Chu, X, Xin, K and Fu, G (2019) Deep learning identifies accurate burst locations in water distribution networks. Water Research 166, 115058. https://doi.org/10.1016/j.watres.2019.115058.CrossRefGoogle ScholarPubMed
Zounemat-Kermani, M, Matta, E, Cominola, A, Xia, X, Zhang, Q, Liang, Q and Hinkelmann, R (2020) Neurocomputing in surface water hydrology and hydraulics: A review of two decades retrospective, current status and future prospects. Journal of Hydrology 588, 125085.CrossRefGoogle Scholar
Figure 0

Table 1. The joint research centre AI taxonomy and relevant applications for UWI

Figure 1

Figure 1. Use of four AI analytics to improve urban water infrastructure performance.

Figure 2

Figure 2. Five pathways towards more reliable, sustainable and resilient urban water infrastructure underpinned by artificial intelligence.

Figure 3

Figure 3. Practical implications and barriers for AI adoption in the water sector.

Author comment: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R0/PR1

Comments

No accompanying comment.

Review: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R0/PR2

Conflict of interest statement

Reviewer declares none.

Comments

The article provides a review of how AI could be aligned to support the future development of urban water infrastructure systems. While the article highlights certain areas of UWI that AI can support, it lacks any specifics on which AI technologies and how AI will support the development of UWI systems. There are many claims in UWI areas that AI can support with limited details or examples. There are too many generic statements and claims about AI’s capabilities and potential, with limited support from the literature or details on specific AI technologies or methods. Most sections provide 3-5 examples from the literature on common UWI challenges or some examples of AI usage in this domain. The article lacks a comprehensive review of the literature but rather provides some examples to highlight the potential of AI. Without a comprehensive review of the entire literature on applications of AI in UWI and novel AI methods from other fields and how they can be applied to UWI challenges, it is hard to justify the statements on AI’s potential and promise in UWI.

Review: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R0/PR3

Conflict of interest statement

Reviewer declares none.

Comments

I apologize for the substantial delay in completing this review. The paper presents a perspective on the role of artificial intelligence (AI) in improving urban water infrastructure (UWI) performance and helping shape future UWI. The authors first identify and explain three dimensions of UWI performance, i.e., reliability, resilience, and sustainability. Second, they analyze how AI can contribute to more reliable, resilient, and sustainable UWI via five development pathways, i.e., decentralization, circular economy, decarbonization, greening, and automation. Finally, they analyze the overall benefits, practical implications, and barriers for AI adoption in the water sector. The topic of the paper is potentially interesting and the paper within the scope of this journal. Also, the paper is generally well written and rather easy to read. Hence, I would like to thank the authors for pulling together this article, which can be interesting for both researchers and practitioners. However, I believe certain aspects (detailed below) need to be revised to mainly (i) explain better the scope of this paper (is it a review paper or another type of paper), and (ii) better explain and report on potential advantages of AI compared to other solutions in a more quantitative way. Finally, I suggest some additional literature that the authors might consider for analysis in their paper.

MAIN COMMENTS

1. The authors call this paper a review. It is, in fact, classified as an overview review. However, it is not explained how the authors collected the literature used in this paper. As this is not a systematic review, I do not expect a fully reproducible and thoroughly detailed explanation. However, it would still be interesting to know if any literature search and analysis procedure was followed. What was included and what was not? This would better define the scope of this review.

2. The authors mention five development pathways (decentralisation, circular economy, greening, decarbonisation, and automation) several times in the paper, already in the first sections. However, they are analyzed in detail only in section 3. I would therefore suggest adding a short definition for each of them already early in the paper to avoid ambiguous interpretation by the readers.

3. The authors properly define AI for the scope of this paper in lines 87-89. I am wondering whether they used any reference to come up with this definition. If so, it would be great if such a reference could be added there.

4. Following up on the previous comment, while AI is defined in the paper and it should be the key focus (it is also in the title), the authors sometimes also use terms like machine learning, and AI analytics (e.g., in the caption of Figure 1). To my understanding and knowledge, machine learning is a sub-set of AI technologies, which also includes deep learning (thus deep learning is a subset of machine learning). However, it looks to me that the authors use machine learning and AI somehow interchangeably in the paper. It would be useful if they can clarify and define how machine learning differs from general AI in this paper. The same goes with “AI analytics.”

5. While section 3.6 provides a general overview of the fundamental attributes that distinguish AI from other technologies, I have the feeling that the current paper generally deals more with explaining the needs of UWI to become more reliable, resilient, and sustainable, rather than explaining how AI can contribute to this in a quantitative way. I wish there was more quantitative analysis of the advantages of AI compared to other (more traditional) technologies on specific relevant problems in UWI. Could examples be added to the paper based on the literature? For instance, examples could report (i) how much of a computational gain can be brought by AI-based surrogate models of water distribution systems, in comparison to physically based hydraulic models, or, (ii) how AI enabled failure detection from image recognition, or (iii) how more accurate predictions of water demand can be achieved by AI methods in comparison to more traditional time series analysis. These are just some examples, but what I think would be useful would be for the authors to provide quantitative evidence of how AI can outperform other techniques in solving some of the main open problems in UWI.

6. In relation to the above comment, I have the impression that some statements support the idea that AI can improve future UWI, but it is not explained “how” and “why AI is needed for that”. For instance, in lines 314-316, the authors say that “AI could be used to capture public perceptions of decentralized wastewater treatment systems”, but it is not clear how this can be achieved by AI (which data are needed, for instance) and why AI can achieve this while other methods cannot.

7. Possibly, the authors might want to consider adding a table summarizing the main benefits and challenges of AI for UWI development, to complement the extensive text, especially if examples as per my comment #5 above will be added in the main paper.

8. The authors explain in lines 184-186 that AI has been used to investigate the potential drivers of water demand. There is also abundant literature about AI methods for predicting water demands, which might be worth mentioning (see, e.g., the section on urban water demand prediction in Zounemat-Kermani et al. (2020) in the additional references I provide below).

Additional references for consideration:

• On AI for urban water demand prediction: Zounemat-Kermani, M. et al. Neurocomputing in surface water hydrology and hydraulics: A review of two decades retrospective, current status and future prospects. J. Hydrol. 125085 (2020).

• On intelligent water systems: Stewart, R. A. et al. Integrated intelligent water-energy metering systems and informatics: Visioning a digital multi-utility service provider. Environ. Modelling Softw. 105, 94–117 (2018).

• On surrogate models (including deep learning) for urban water systems:

o Fiedler, F., Cominola, A., & Lucia, S. (2020). Economic nonlinear predictive control of water distribution networks based on surrogate modeling and automatic clustering. IFAC-PapersOnLine, 53(2), 16636–16643.

o Garzón, A. et al. “Machine learning-based surrogate modelling for Urban Water Networks: Review and future research directions.” Water Resour. Res. (2022): e2021WR031808.

Recommendation: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R0/PR4

Comments

Thank you for submitting your manuscript. Two highly qualified reviewers have provided detailed comments on your paper. Both suggest that the review is not comprehensive and systematic enough to be accounted for as a review paper. Both reviewers also agree that the statements related to AI improving UWI performance while important, it is not backed up by enough details on why and how and citations for those details. I suggest you closely review the comments provided by the reviewers and revise your paper accordingly.

Decision: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R0/PR5

Comments

No accompanying comment.

Author comment: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R1/PR6

Comments

No accompanying comment.

Review: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R1/PR7

Conflict of interest statement

Reviewer declares none.

Comments

While the authors put some effort into addressing the comments from reviewers, the article still lacks critical information about the review procedure and methodology. Limited information is provided in the introduction section about the review process, which should be detailed in the methods section. The methodology, as explained in the introduction section, is also flawed in terms of coverage. Searching for “water” and selected AI keywords in the title will yield limited amounts of articles, which could lead to limited insights about the literature. Many papers on UWA may not use “water” in the title but use other critical keywords about UWI in the title or abstract. Just “machine learning” studies in the water domain could yield several thousands of articles. The entire UWI domain could easily have tens of thousands of articles.

It looks like a comprehensive review is not the goal of this study. I suggest reclassifying this paper as a vision or position paper (if the journal allows) and evaluating accordingly. In its current form, it doesn’t satisfy the expectations of a comprehensive review or overview review paper.

Review: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R1/PR8

Conflict of interest statement

Reviewer declares none.

Comments

The authors improved the manuscript and implemented suitable changes to address all my comments. I believe this can be an interesting overview paper worth publication after minor changes as per my two comments below:

• I appreciate the authors’ efforts in editing the introduction to clarify that this paper is an overview review and not a systematic review. However, for better transparence and clarity, more details about their paper search and selection procedure are needed. Not necessarily a full PRISMA diagram, but some data in the text about the following points: (i) which specific keywords and keyword combinations were used for the paper search? (ii) how many papers were obtained from the paper search? How many after including other papers identified with the snowballing method? (iii) how many papers were then included in each of the four analytics and in each of the five pathways? Information on all these points would help communicating the rationale behind each step of the search and review methods.

• The authors cite the IWA Digital Water report (line 33-34, page 3) to support their statement about digital transformation and Water 4.0. This is a suitable reference, yet it’s a non-peer-reviewed publication as far as I know. I would thus suggest also adding a reference to the following two - more recent and peer-reviewed – publications on the topic:

o Daniel, I., Ajami, N.K., Castelletti, A. et al. A survey of water utilities’ digital transformation: drivers, impacts, and enabling technologies. npj Clean Water 6, 51 (2023). https://doi.org/10.1038/s41545-023-00265-7

o Rapp, A.H., Capener, A.M. and Sowby, R.B., 2023. Adoption of Artificial Intelligence in Drinking Water Operations: A Survey of Progress in the United States. Journal of Water Resources Planning and Management, 149(7), p.06023002.

Recommendation: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R1/PR9

Comments

Thank you for the efforts you dedicated to revising your manuscript. I am sending this back to you for another round of revision as both reviewers have provided additional constructive feedback which I believe would improve this manuscript further. I especially note the comment by the first review on searching for “water” and selected AI keywords not only in the title but also in the abstract or even the entire paper. That may significantly improve your search results and the number of papers that fall under this category.

Decision: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R1/PR10

Comments

No accompanying comment.

Author comment: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R2/PR11

Comments

No accompanying comment.

Review: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R2/PR12

Conflict of interest statement

Reviewer declares none.

Comments

The authors have successfully responded to the review comments.

Review: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R2/PR13

Conflict of interest statement

Reviewer declares none.

Comments

The authors addressed my remaining comments and I thus recommend accepting this revised version of their paper.

Recommendation: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R2/PR14

Comments

Thank you for your submission. We appreciate your effort to revise your paper based on the reviewer’s comments. I am pleased to accept your paper.

Decision: Artificial intelligence underpins urban water infrastructure of the future: A holistic perspective — R2/PR15

Comments

No accompanying comment.