The Role of Smart Infrastructure in Residential Water Demand Management: A Global Survey
Abstract
1. Introduction
- High-resolution data collection over smart metering to capture granular, time-stamped water use configurations.
- Behavioral and socio-demographic investigation to find high-consumption parts (e.g., small, older households) and patterns of incompetent usage.
- Disaggregated end-use modelling, allowing exact credit of demand to specific activities such as showers, laundry, and irrigation.
- Efficiency-based interference, including the elevation of water-saving applications and detection of non-compliant irrigation performs.
- Temporal demand profiling, using daytime water use patterns to update infrastructure design, peak-demand management, and strategy timing.
- Equity-aware design, accounting for varied local, demographic, and household characteristics that affect water stress levels.

2. Methodology
2.1. Research Questions
2.2. Literature Search Strategy
3. Global Motivations for WDM
3.1. Overview
3.2. Role of Policies and Regulations in WDM Adaptation
4. Assessment of Current Techniques in Smart WDM
5. Smart Agents for WDM
5.1. Smart City Concept
5.1.1. Smart Water Management (SWM)
5.1.2. Smart Water Management at Residential Buildings
5.1.3. Information and Communication Technologies (ICT)
5.1.4. IoT
- Connectivity: Connecting sensors to the cloud and other “things” has never been easier because of the proliferation of network protocols for the internet.
- Cloud computing systems: The proliferation of cloud platforms gives companies and individuals easy access to scalable infrastructure without the overhead of managing it themselves.
- Analytics and ML: Businesses now have easier and quicker access to valuable insights due to developments in ML and analytics, as well as the diverse and large volumes of data stored on the cloud. The data generated by IoT also fuels these ancillary technologies, whose rise continues to push the frontiers of IoT.
- AI capable of human-like conversation: IoT devices (such as digital personal assistants like Alexa, Cortana, and Siri) now have access to natural language processing (NLP) thanks to developments in neural networks.
5.1.5. Smart Metering
- Detection/transduction system to convert the analytical signal into a measurable electrical quantity.
- Suitable measurement and signal processing interface to shape the electrical signal.
- Data processing together with a calibration system to ensure the measurement is accurate.
- Autonomous power source to guarantee the nonstop operation of the entire process.
5.1.6. Demand Response (DR)
6. Common Barriers of Applying WDM
- (a)
- Lacking in Education and Awareness: The necessity of water conservation and effective distribution practices may not be well known in many areas due to a lack of awareness and education. Because of this, water may be used inefficiently, and distribution systems may not be properly maintained.
- (b)
- Resistance to Change: Stakeholders may be hesitant to adopt new water distribution practices due to their comfort with the status quo. This may be a barrier to implementing new methods of administration and cutting-edge technology.
- (c)
- Inadequate Community Engagement: The effectiveness of water distribution management plans may be hampered by a lack of active engagement and involvement from local communities, which is often the result of Inadequate Community Engagement. Sustainable water management relies heavily on public participation, education, and involvement in policymaking.
7. Conclusions
Author Contributions
Funding
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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| Criteria | Centralized WDM | Decentralized WDM | References |
|---|---|---|---|
| Decision-Making | Top-down, single authority | Bottom-up, individual users | [20] |
| Efficiency | High system-wide optimization | Moderate individual optimization | [21] |
| Cost | High due to infrastructure and management overhead | Lower upfront and operational costs | [22] |
| User Engagement | Low (limited user input) | High users actively participate | [21] |
| Equity/Fairness | May lack fairness due to one-size-fits-all mandates | High fairness through local customization | [23] |
| Resilience | Vulnerable to system-wide failures | More resilient due to Localized autonomy | [24,25] |
| Scalability | Scales well with central planning | May face challenges at large scale | [21,26] |
| Environmental Impact | May struggle with local sustainability and nutrient recovery | More adaptable to ecological design | [24,27] |
| Effectiveness | High effectiveness in control and consistency | High effectiveness in adaptability and resilience | [28,29] |
| Concept | Definition | Key Thresholds | Main Drivers | Smart-MISS Response |
|---|---|---|---|---|
| Water Scarcity | Insufficient availability of renewable freshwater resources to meet wants | <1700 m3/cap/yr (scarcity), <500 (absolute) | Climate, geography, and overuse of sources | Monitors obtainability, informs infrastructure resilience |
| Water Stress | Extreme pressure on available water resources due to extractions | >25% withdrawal (moderate), >100% (critical) | Population growth, lifestyle, and inefficient use | Targets mandate decrease, promote conservation behaviors |
| Definition | Definition Type | Source |
|---|---|---|
| When individuals lack access to sufficient, safe, and affordable water for personal or livelihood needs, the area is considered water scarce. | Access-Based | [47,55,56,57] |
| Scarcity occurs when aggregate user demands (including environmental) cannot be met due to limitations in supply or institutional arrangements. | Institutional/UN Definition | [58,59] |
| Defined by the marginal value of water, it is the opportunity cost of not having an additional unit of water. | Economic (Marginal Value) | [60] |
| There is insufficient water to meet all demands. | Physical Scarcity | [56] |
| Water is physically available, but access is limited by a lack of investment or institutional capacity. | Economic Scarcity | [47] |
| It is the yearly accumulated difference between daily water demand and availability. A persistent gap leading to resource depletion defines water scarcity. | Quantitative (Water Gap) | [61] |
| Water scarcity is shaped and often manufactured by political and institutional processes that marginalize certain populations. | Governance-Based | [62] |
| Influence Factors | Contents | Details |
|---|---|---|
| The external environment | Geographical environment Climate environment | Longitude, latitude, altitude temperature, humidity |
| Water supply and drainage system | Water supply and drainage facilities Water-saving measures Water supply and drainage management | Domestic water, irrigation water Reuse of recycled water and rainwater Management level, intelligent control system |
| Building design | Building design, shape, landscape | Various buildings like residential, commercial, and public buildings Shape, area, number of layers |
| Human dimensions | Life habit Other factors | Cultural qualities, energy-saving awareness, income |
| Study | [96] | [97] | [98] | [99] | [100] | [101] | [102] | [103] | |
|---|---|---|---|---|---|---|---|---|---|
| Parameter | |||||||||
| Water Level | ✓ | ✓ | ✓ | ✓ | ✕ | ✕ | ✕ | ✕ | |
| pH | ✕ | ✕ | ✕ | ✕ | ✓ | ✓ | ✓ | ✓ | |
| Dissolved Oxygen | ✕ | ✕ | ✕ | ✕ | ✓ | ✓ | ✕ | ✕ | |
| Turbidity | ✕ | ✕ | ✕ | ✓ | ✓ | ✓ | ✕ | ✕ | |
| Conductivity | ✕ | ✕ | ✕ | ✓ | ✓ | ✓ | ✓ | ✕ | |
| Redox Potential | ✕ | ✕ | ✕ | ✕ | ✓ | ✕ | ✕ | ✕ | |
| TDS | ✕ | ✕ | ✕ | ✕ | ✕ | ✕ | ✓ | ✕ | |
| Chlorophyll | ✕ | ✕ | ✓ | ✓ | ✕ | ✓ | ✕ | ✕ | |
| Temperature | ✕ | ✕ | ✕ | ✓ | ✕ | ✓ | ✕ | ✓ | |
| Salinity | ✕ | ✕ | ✕ | ✕ | ✓ | ✕ | ✕ | ✓ | |
| Flow rate (Litre/S) | ✕ | ✕ | ✕ | ✕ | ✕ | ✕ | ✕ | ✕ | |
| Algorithm/Model | Application Context | Performance Indicators | Strengths | Reference |
|---|---|---|---|---|
| VS-SVR | Dynamic daily urban water consumption forecasting | MAE = 5320.7 m3/day; MAPE = 2.65%; RMSE = 7048.6 m3/day; R2 ≈ 0.93 | Dynamic model adapts to changing conditions; 33% RMSE reduction over static LSSVR | [113,114] |
| Deep Neural Network (LSTM-based) | Unsupervised anomaly detection in SWaT plant | Precision = 0.91; Recall = 0.80; F1 = 0.86 | Fewer false alarms; captures nonlinear temporal patterns | [114] |
| SVM (Base Model) | Time-series regression | RMSE = 682.63; MSE = 467,214.38; MAE = 597.96; R2 = 0.30; MAPE = 2.47% | Stable linear regression baseline | [115] |
| LSTM (Base Model) | Time-series regression | RMSE = 399.39; MSE = 159,519.52; MAE = 356.04; R2 = 0.76; MAPE = 1.41% | Learns long-term dependencies; high accuracy | [115] |
| LSTM (Advanced + Moving Averages) | Combined time-series dataset | RMSE = 347.46; MSE = 120,731.41; MAE = 262.42; R2 = 0.83; MAPE = 1.03% | Best overall accuracy; robust for multivariate data | |
| Backpropagation ANN | Short-term forecasting and classification | Accuracy = 68.6%; SD = 0.55; Time = 12.6 s | Fast convergence; simple architecture |
| Tariff Mechanism | Definition | Purpose/Rationale |
|---|---|---|
| Fixed Charge | A constant fee is charged regardless of consumption | Ensures basic revenue for utility |
| Volumetric Pricing | Users pay per unit of water consumed | Promotes conservation, links cost to use |
| Increasing Block Tariff (IBT) | Price per unit increases with higher usage (e.g., blocks of m3) | Encourages conservation, supports equity |
| Decreasing Block Tariff | Price per unit decreases with higher usage | Favors large users, promotes economies of scale |
| Two-Part Tariff | Combines a fixed charge and a variable (volumetric) component | Balances cost recovery and consumption-based billing |
| Seasonal Tariffs | Higher rates in peak season (e.g., summer), lower in off-peak | Reflects supply stress and scarcity during certain times |
| Quota-Exceeding Tariff | Users are allocated a quota, with higher rates above that | Discourages overuse beyond “essential” need |
| Flat Fee | Single fixed amount per month, regardless of use | Simplicity, but lacks conservation signal |
| Free Allowance/Lifeline Tariff | The initial volume of water (e.g., 10–20 m3) provided at low or zero price | Basic human rights, affordability |
| Marginal Cost Pricing | Price reflects long-run marginal cost of water provision | Economic efficiency, cost-reflective pricing |
| Market-Based Pricing | Water rights or permits are bought and sold | Reflects true market value, allocates efficiently |
| Subsidized Block Pricing | Lower prices for lower-income households in initial block | Promotes affordability and equity |
| Index-Linked Tariffs | Tariffs adjusted regularly based on inflation or cost index | Keeps tariffs sustainable over time |
| Wastewater Tariffs (Add-on) | Separate charge for wastewater treatment | Ensures environmental cost recovery |
| Pollutant-Based Charges | Fees based on volume and concentration of pollutants discharged | “Polluter Pays Principle”, incentivizes cleaner processes |
| Country | Pricing Basis | Main Sectors | Cost Recovery Focus | Environmental Pricing | Social Equity Consideration | Key Challenges |
|---|---|---|---|---|---|---|
| Australia | State-based, national framework | Urban, irrigation | High | Medium | Medium | Variability, drought regulation |
| Brazil | River basin (ANA) | All | Medium | Low | Medium | Regional disparities |
| Canada | Local/province | All | Low to Medium | Low | Medium | Low price incentives |
| Chile | Market-based | Urban, agriculture | High | Medium | Low | Groundwater management |
| China | Central and local hybrid | All | Medium | Low | Medium | Institutional overlap |
| Colombia | Centralized (post-1994) | All | High | Low | High | Implementation of tariff reforms |
| France | National system | Urban, agriculture | Medium | Medium | High | Pricing complexity |
| India | State jurisdiction | Irrigation, urban | Low | Low | Medium | Low pricing efficiency |
| Italy | Decentralized | Urban, industry | Medium | Low | Medium | Investment support via taxes |
| Mexico | Regional zones | All | Medium | Medium | Medium | Sector equity |
| Netherlands | National taxes + pricing | Domestic, industry | Medium | Medium | Medium | Fiscal efficiency |
| New Zealand | Local control | Urban, irrigation | Low to Medium | Low | Medium | Irrigation water scarcity |
| South Africa | National + local tier | All | Medium | Medium | High | Implementation & affordability |
| Spain | National + EU directive | All | Medium | High | Medium | Climate adaptation, CAP linkages |
| Saudi Arabia | Nationally regulated | Urban, agriculture | Low | Low | High | Heavy subsidies, low tariffs |
| GCC Countries | National frameworks | Urban, agriculture | Low | Low | Medium | Low-cost recovery, high consumption |
| Egypt | Centralized | Urban, agriculture | Medium | Low | High | Low tariffs, high subsidies |
| Yemen | Local corporations | Urban, agriculture | Low | Low | Low | Weak enforcement, over-extraction |
| Key Points | Definitions | References |
|---|---|---|
| IoT-based system | There are alternatives to manual metering systems, and these include smart water systems. These are examples of wireless sensor networks, in which water meters in thousands of homes gather data at regular intervals and relay that information in real time to a central database. Water temperature, phosphate, dissolved oxygen, conductivity, pH, turbidity, and water-level sensors may all be integrated into the “SmartCoast” Multi-Sensor System for water quality monitoring. ThingSpeak is a cloud-based IoT analytics solution that enables the collection, visualization, and analysis of real-time data streams. The ThingSpeak platform provides access to MATLAB analysis, which computes statistics like the lowest, maximum, and average amounts of water consumed daily, weekly, and monthly. | [125,178,179] |
| AI-IoT–enabled WDS | Building managers can keep tabs on water use and demand, as well as examine the efficiency of their water systems, with the help of AI-enabled IoT water management systems. The water quality index fluctuation can be explained by the Support Vector Machine (SVM) models 87% of the time. SVM’s findings may potentially be used to better manage rivers to ensure a high-quality water supply. In Ohio, USA, AI is used in conjunction with IoT data on water levels, flow, and storage capacity across stormwater and combined sewer collection networks to create a wet weather management system. This aids in the monitoring of utility networks and the optimization of storage capacity to avoid floods and overflows during rainy weather events. | [180,181,182] |
| Water Smart meters | The smart water meter’s prototype includes a microprocessor, a Wi-Fi module, a water flow sensor, and a GPS module. One of the most well-known and widely applied stochastic time series models, the autoregressive integrated moving average (ARIMA), captures a variety of common temporal features in time series data. When it comes to fine-tuning Holt’s Winter method’s coefficients, deep learning techniques like the Recurrent Neural Network (RNN) and its variant, the Long Short-Term Memory (LSTM), are able to learn predictions from sequences of data. | [115,183,184,185,186] |
| Efficiency in IoT technology | From the outset, power is fed into the system from the generator. When the ultrasonic sensor has been properly calibrated, the system may begin functioning. A model of a physical system that is stored digitally. Clustering and Kohonen networks are used in an integrated water and energy forecasting model to provide accurate predictions of future water and energy needs. | [187] |
| Application of AI in WDM | The goal of ML in the field of AI is to enable the development of systems that can generalize behavior based on examples presented in an unstructured style. Inside it, in 2002, NNs were employed to predict the highest possible weekly demand based on weather conditions (water temperature, frequency, and volume of rainfall), as well as on demand levels from the previous years. The bulk of the published methodologies in the literature regarding AI applied to WDM are based on demand forecasting. | [188,189] |
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Alzahrani, A.; Alogla, A.; Aljlil, S.; Alshehri, K. The Role of Smart Infrastructure in Residential Water Demand Management: A Global Survey. Water 2025, 17, 3119. https://doi.org/10.3390/w17213119
Alzahrani A, Alogla A, Aljlil S, Alshehri K. The Role of Smart Infrastructure in Residential Water Demand Management: A Global Survey. Water. 2025; 17(21):3119. https://doi.org/10.3390/w17213119
Chicago/Turabian StyleAlzahrani, Ateyah, Ageel Alogla, Saad Aljlil, and Khaled Alshehri. 2025. "The Role of Smart Infrastructure in Residential Water Demand Management: A Global Survey" Water 17, no. 21: 3119. https://doi.org/10.3390/w17213119
APA StyleAlzahrani, A., Alogla, A., Aljlil, S., & Alshehri, K. (2025). The Role of Smart Infrastructure in Residential Water Demand Management: A Global Survey. Water, 17(21), 3119. https://doi.org/10.3390/w17213119

