1. Introduction
Water stress in semi-arid regions is a global management challenge, as rising climate variability, demand pressures, and uneven monitoring capacity increasingly affect water availability and service reliability across arid and semi-arid settings. In Latin America, these pressures are compounded by hydrological variability, rapid urban growth, and uneven infrastructure, which increase exposure to droughts and service intermittency [
1]. In these contexts, “water scarcity” is not only a physical constraint but also a management challenge shaped by limited observability, operational inefficiencies, and governance fragmentation [
2,
3,
4,
5]. These pressures highlight cross-sector interdependencies and reinforce the need for integrated WRM approaches that remain feasible under constrained institutional capacity [
6].
Peru—particularly Piura-like coastal semi-arid settings—illustrates how limited observability of basin dynamics and distribution networks can constrain timely decision-making and effective enforcement [
7]. These constraints are amplified by overlapping mandates and unequal technical capacity across actors, which weakens coordination and implementation. Evidence from water-scarce cities further shows that resilience is not achieved solely through additional supply; it depends on service reliability, risk management, and the institutional ability to coordinate, prioritize, and learn from interventions [
5,
8,
9]. These pressures are intensified by climate-driven extremes and persistent data gaps, thereby reducing the capacity to anticipate drought/flood impacts, verify compliance, and target investments efficiently [
10,
11].
In parallel, digitalization is accelerating in sustainability research, positioning smart technologies as enablers of transparent, efficient, and adaptive resource management. Evidence links this transformation to improved sensing, analytics, automation, and decision support, contingent on interoperability, data governance, and sustainable operations and maintenance (O&M) [
12,
13,
14,
15]. In WRM, this translates into near real-time situational awareness and performance-based management across basin and utility levels [
15,
16,
17,
18].
This digitalization shift is reflected in the smart WRM literature, which can be organized into three application-oriented technology families. First, remote sensing and GIS extend hydrometeorological and hydrogeological assessment where ground networks are sparse, enabling drought-related indicators, basin diagnostics, and spatial screening for planning [
19,
20]. This line of work increasingly combines geospatial workflows with AI to improve interpretation and actionable insights, particularly under data scarcity and non-stationarity [
21]. Second, IoT and telemetry strengthen operational control and environmental surveillance through sensor networks, smart metering, and SCADA-linked instrumentation for anomaly detection, water quality surveillance, and faster response [
22,
23]. Third, analytics and AI-enabled decision support systems enhance forecasting, anomaly detection, and risk management; evidence from water quality modeling shows sustained growth in ML applications alongside ongoing challenges in interpretability, generalizability, and data quality [
24,
25].
Despite this progress, the evidence base remains uneven in two ways that matter for Peru and comparable semi-arid territories. On the one hand, measurable operational outcomes are more consistently documented—such as improvements in early warning timeliness, forecasting accuracy, water quality surveillance, and NRW/leakage detection—especially where IoT is integrated with automation and asset management practices [
26]. On the other hand, governance-related effects—particularly allocation and compliance, and less consistently transparency, participation, and accountability—are less consistently measured and often remain implicit, even though the enabling conditions—data interoperability, institutional coordination, and sustainable O&M financing—are repeatedly identified as decisive [
27,
28]. In resource-constrained settings, “pilot fatigue” is a practical risk: projects demonstrate technical feasibility but fail to scale because data pipelines, responsibilities, and budgets are not institutionalized [
29,
30,
31].
Accordingly, a focused synthesis is needed on smart technologies that strengthen water resources management in Peru and comparable Latin American semi-arid contexts.
Unlike broader smart-water reviews, this review focuses on basin- and utility-level WRM in semi-arid settings, using Peru as an anchor case within a Latin American comparative lens. It synthesizes peer-reviewed evidence from 2020 to 2026 on measurable operational and governance outcomes and the barriers that shape movement from pilot projects to policy-relevant adoption pathways [
32].
The objective is to identify which smart technology applications have demonstrated measurable operational and governance improvements for WRM in semi-arid settings and which enabling conditions support scale-up.
This review addresses three guiding questions: (i) What measurable operational and governance outcomes are reported for smart technology applications in basin- and utility-level WRM in semi-arid Latin American contexts (2020–2026)? (ii) Which application-oriented technology families and application areas dominate the evidence base (remote sensing/GIS, IoT/telemetry, analytics/AI-enabled DSS)? (iii) What barriers and enabling conditions shape implementation quality, integration, and scale-up from pilots to policy-relevant adoption—particularly regarding interoperability, institutional coordination, digital capacity, and sustainable O&M financing?
2. Materials and Methods
This section describes the scope and review design, eligibility criteria, information sources, search strategy and execution, record management (export, deduplication, and screening), and the data extraction and coding approach used to support narrative synthesis.
2.1. Scope and Review Design
This narrative review synthesizes peer-reviewed evidence published between 2020 and 2026 on smart technologies that support basin- and utility-level water resources management (WRM) in semi-arid contexts. This time window was selected to capture the most recent and policy-relevant phase of smart WRM research. It prioritizes contemporary evidence on measurable outcomes, implementation barriers, and scale-up conditions rather than earlier stages of digital-water development. Peru (Piura-like coastal settings) is used as an anchor case, with Latin America as the main comparative lens. To avoid missing transferable evidence, we also retained a limited set of globally relevant studies when they explicitly addressed semi-arid WRM applications and reported measurable outcomes.
The scope covers smart technology applications for WRM at basin and utility levels in semi-arid contexts. We prioritize studies reporting measurable operational outcomes and, when available, governance-related effects. Here, smart technologies for WRM are defined as digital and data-enabled solutions supporting five application categories plus an other label used for coding and synthesis: early warning, forecasting, water quality, NRW leakage, allocation and compliance, and other. For consistency, the master dataset used standardized labels.
Evidence is grouped into three technological families: (1) remote sensing and GIS, (2) IoT/telemetry (including SCADA/AMI), and (3) analytics/AI and decision support systems (DSS). This review is narrative in its synthesis logic and interpretive purpose, as it aims to organize heterogeneous evidence into an application-oriented framework and draw context-sensitive implications for semi-arid WRM. Study identification and selection followed a structured process informed by PRISMA guidance and aligned with the SALSA logic for systematized reviews (Search, Appraisal, Analysis, and Synthesis), adapted to the review objectives and the semi-arid WRM context [
33]. This structured component was used to improve transparency, consistency, and traceability in evidence selection and organization, rather than to frame the study as a full systematic review. The overall methodological sequence is summarized in
Figure 1.
2.2. Eligibility Criteria
Eligibility criteria were defined a priori to ensure relevance to WRM, support consistent screening, and improve transparency and traceability across selection decisions. Exclusions were documented using standardized reasons in the master dataset to maintain consistency across title/abstract and full-text screening.
2.2.1. Inclusion Criteria
Time window: 2020–2026.
Document type: peer-reviewed journal articles (original research and reviews) and conference-derived publications were eligible only when methods and results were reported with sufficient clarity to support evidence extraction and coding; conference-derived records were not retained on document type alone.
WRM scope: basin- and utility-level WRM in semi-arid contexts (or clearly transferable settings).
Technology scope: remote sensing (RS) and GIS; IoT/telemetry (including SCADA/AMI); analytics/AI; decision support systems (DSSs).
Evidence requirement: reports at least one measurable outcome aligned with the coded application areas (early warning, forecasting, water quality, NRW leakage, or allocation and compliance).
Geographic scope: Peru as an anchor case and Latin America as the primary comparative region; studies from other regions were included only when they examined semi-arid or water-stressed contexts, addressed comparable basin- or utility-level WRM functions, and reported measurable outcomes or implementation conditions relevant to contextual transfer.
2.2.2. Exclusion Criteria
Primarily focused on agronomic productivity or irrigation yield without a clear basin/utility WRM contribution (agriculture or irrigation focus).
Did not report evaluable or measurable outcomes (no measurable outcome).
Not related to smart technologies as defined in
Section 2.1 (not smart technology).
Outside the review boundaries (outside geographic scope, outside the time window, outside WRM scope).
Non-peer-reviewed literature (used only for background framing).
Insufficient information for screening or full-text assessment.
2.3. Information Sources
Searches were conducted in Scopus and the Web of Science Core Collection as the primary bibliographic databases. IEEE Xplore was used as a complementary source to capture engineering-oriented evidence on IoT/telemetry (including SCADA/AMI) and applied analytics relevant to WRM. To reduce omission risk, we screened reference lists of key included studies and examined papers citing them. Searches were executed between late January and early February 2026.
2.4. Search Strategy and Execution
Search strings were built around four concept blocks. The first defined the WRM context and management scale; the second captured the technology domain; the third targeted application and performance terms aligned with the coded outcome areas; and the fourth delimited the geographic lens, using Peru as an anchor and Latin America as the primary comparative region. The queries were then iteratively refined to balance recall and precision [
33].
A core query was executed in each database and complemented by two targeted variants to capture recurring evidence clusters using different terminology: (a) IoT/telemetry for utility networks (NRW/leakage and distribution network management, including SCADA/AMI and related sensing/telemetry terms), and (b) RS/GIS and analytics for hydrometeorological risk (drought/flood; early warning/forecasting). AI/DSS-related studies were captured through the core query and later organized under the analytics/AI + DSS coding family.
Queries were implemented using database-specific fields (Scopus: TITLE-ABS-KEY; Web of Science (WoS): Topic [TS]; IEEE Xplore: metadata/abstract fields as available) and limited to 2020–2026. Records were exported and deduplicated prior to screening. Screening was conducted in two steps: combined title/abstract screening, followed by full-text assessment only when eligibility could not be confirmed from bibliographic information. The database search, deduplication, and primary screening workflow were conducted by the first author using the predefined eligibility criteria and screening protocol. Co-authors contributed through methodological oversight and review of the inclusion logic at key stages of the process. When bibliographic information or study scope raised borderline inclusion questions, these cases were discussed among the authors and resolved by consensus before final retention.
Across databases, 371 records were exported (Scopus n = 186; WoS n = 137; IEEE n = 48), resulting in 207 unique records after deduplication. Screening decisions were recorded by stage (title/abstract screening and full-text assessment). Exclusions were documented using 6 standardized reasons (agriculture irrigation focus, no measurable outcome, not smart technology, outside geographical scope, outside time window, outside WRM scope).
2.5. Data Extraction, Coding, and Synthesis
For each included study, we extracted bibliographic metadata (title, year, source, document type, DOI, abstract, and keywords). Bibliographic metadata were exported from each database using the available structured fields, standardized across sources in a master spreadsheet, and verified during deduplication and screening before coding. The included studies were then coded across the following dimensions:
Geographic scope: Peru, Latin America, globally relevant evidence transferable to semi-arid WRM, or other.
Technology family: (1) remote sensing and GIS, (2) IoT/telemetry (including SCADA/AMI), (3) analytics/AI and decision support systems (DSS), hybrid, or Other.
Application category: early warning, forecasting, water quality, NRW/leakage, allocation and compliance, or Other.
Outcome type: operational, governance, both, or not reported.
Implementation factors: barriers and enablers related to data availability/labeling, interoperability, energy/connectivity, O&M/financing, skills/capacity, and institutional arrangements.
We applied a predefined codebook with standardized labels to support consistent coding across records. A concise coding summary defining the application categories and outcome types used in the review is provided in
Supplementary Materials. Primary coding was conducted by the first author. Co-authors contributed through review of category logic, interpretation of borderline classifications, and critical revision of the coded structure at manuscript-development stages. When a study could plausibly fit more than one category, final coding decisions were discussed among the authors and resolved by consensus to preserve internal consistency. This structured, table-based organization of the evidence base is consistent with systematized review practices [
33]. Findings were synthesized qualitatively. We report directional effects and representative metrics, acknowledging heterogeneity in study designs and outcome measures.
2.6. Quality Considerations
Given the narrative design and heterogeneity in study types and outcome measures, we assessed robustness through transparent criteria rather than a single standardized critical appraisal checklist, consistent with guidance for narrative reviews that emphasize search transparency and the presentation of relevant evidence [
34]. Specifically, we considered: (i) clarity of data sources and study setting, that is, whether the empirical context, data origin, and application setting were clearly identifiable; (ii) methodological reporting, including the description of data, models, and validation approach; and (iii) outcome reporting, including defined metrics, baselines, and evaluable performance evidence. During synthesis, greater weight was given to studies with explicit evaluation protocols and measurable outcomes, while descriptive or purely conceptual contributions were used only for contextual framing.
4. Discussion
According to the reviewed evidence, smart technologies consistently improve operational functions in semi-arid WRM, especially observability, timeliness, forecasting, and decision support. However, scale-up and sustained impact depend on conditions beyond the tools themselves. Across the corpus, the evidence is stronger for performance improvements than for governance outcomes. This section therefore focuses on the main constraints and enabling conditions shaping implementation: technical readiness (data quality, interoperability, and connectivity), long-term sustainability (O&M capacity and lifecycle costs), and institutional and governance conditions (roles, coordination, accountability, and response protocols). Together, these factors help explain why many solutions remain at pilot stage and why scale-up depends on broader territorial readiness.
This pattern is consistent with evidence beyond Peru and Latin America. Across contexts, the clearest reported effects remain operational, while governance-related effects are less frequently measured and more dependent on institutional conditions. Sustained impact, in turn, depends on data quality, interoperability, reliable connectivity, and long-term institutional and O&M capacity [
49,
50,
75,
103].
Figure 2 summarizes how operational gains translate into durable WRM improvements only when cross-cutting scale-up conditions are in place.
4.1. Technical Readiness Constraints: Data, Interoperability, and Connectivity
A recurrent limitation across the reviewed evidence is that technical performance is often demonstrated under data and system conditions that are difficult to replicate in semi-arid territories. In practice, scale-up depends on whether WRM pipelines can be fed with reliable data, integrated with existing operational platforms, and sustained under connectivity and energy constraints.
Data readiness and validation are a first binding constraint. In many studies, performance gains depend on calibration, ground observations, and transparent validation. This is especially true for satellite or gridded products in sparsely gauged basins [
37,
48,
87,
105]. Without stable data quality assurance and control (QA/QC) and repeatable validation, uncertainty increases. Outputs then become harder to trust and harder to operationalize in routine decision-making.
Interoperability with legacy systems is a second constraint. Even when sensing or analytics are technically sound, value is limited if outputs cannot be integrated into existing telemetry, GIS, and operational dashboards. In the reviewed corpus, utility-oriented implementations repeatedly highlight the need to connect field devices, communications layers, and monitoring/control interfaces. Otherwise, insights remain “parallel” products rather than embedded decision inputs [
67,
69,
70,
74,
81].
Connectivity and energy reliability form a third constraint, especially in dispersed and remote monitoring settings. IoT deployments repeatedly report intermittent communications, limited coverage, and infrastructure fragility. These factors threaten data continuity and system uptime. As a result, early warning and operational control weaken precisely when reliability is most needed [
66,
68]. The broader smart-water IoT literature reports the same pattern, particularly in low-resource or hard-to-reach settings [
17,
28].
Overall, technical readiness is less about deploying devices or models than about establishing a dependable socio-technical pipeline. That pipeline must connect data generation, validation, system integration, and delivery of actionable information. Without it, promising performance indicators are unlikely to translate into sustained WRM improvements at scale [
37,
81].
4.2. Long-Term Sustainability Constraints: O&M Capacity and Lifecycle Costs
A second set of constraints concerns whether smart WRM solutions can be operated and financed reliably over time, beyond initial deployment and integration. Evidence on smart water management and digitalization barriers repeatedly shows that technical feasibility is not enough. Long-term value depends on sustained O&M capacity and recurrent financing that covers the full lifecycle of hardware, software, and data services [
12,
24,
28].
O&M capacity and service arrangements are a first bottleneck. Field deployments require routine calibration, replacement cycles, and continuous configuration of dashboards, alerts, and data services. Low-cost architecture can reduce entry barriers, but they still require stable maintenance routines and clearly assigned responsibilities. Without these, performance drift and data degradation accumulate over time [
22,
101]. This point is also emphasized in smart-water IoT reviews, where upkeep requirements and operational continuity are recurrent determinants of real-world feasibility, especially in low-resource settings [
28].
Lifecycle costs and recurrent financing are a second bottleneck. Many pilots prioritize upfront procurement, while recurrent cost drivers—connectivity, hosting, licenses, cybersecurity updates, spare parts, and periodic upgrades—are underestimated or not institutionalized in annual budgets [
14,
28]. Funding models also matter. Decision support creates value only if the service remains available across seasons and extremes, consistent with climate-service evidence for reservoir management, where sustained delivery underpins adoption [
77]. Similarly, cost-effective AMI can reduce entry barriers, but it still requires ongoing service and replacement over the system lifetime [
69].
Overall, operational and financial sustainability often determines whether a smart WRM solution remains a demonstrator or becomes institutionalized infrastructure. When O&M capacity and lifecycle funding are not designed upfront, and matched with realistic service levels, solutions tend to remain fragile pilots rather than durable operational systems [
14,
28].
4.3. Institutional and Governance Constraints—And Enabling Conditions for Scale-Up
A third set of constraints is institutional and governance-related. Smart WRM tools generate sustained value only when information is translated into coordinated decisions, field actions, and compliance across multiple actors. Evidence on IWRM performance and adaptive governance suggests that governance outcomes are often less visible than operational gains. This is because implementation depends on mandates, coordination capacity, and accountability mechanisms, not only on technical performance [
8,
11].
Roles, coordination, and accountability are recurrent bottlenecks. Basin- and utility-level responsibilities are often distributed across agencies and levels of government. This can fragment decision rights and blur ownership of data and actions. When it is unclear who validates information, who triggers response, and who is accountable for outcomes, decision-support outputs remain advisory rather than actionable. As a result, gains in monitoring, early warning, and forecasting do not consistently translate into timely response and enforcement [
7,
11,
15].
Protocols and institutionalization of workflows are equally critical. Smart tools can improve visibility and timeliness, but sustained impact requires standard operating procedures, thresholds, and escalation pathways that define what happens when indicators change. Without agreed response protocols and routine operational use, systems remain intermittent add-ons rather than institutional infrastructure [
14,
18].
Policy pathways and enabling conditions therefore matter for scale-up. Work on governance innovation in smart water management emphasizes the need for explicit rules for data access and sharing, standard operating procedures, and coordination protocols [
15]. These elements help connect technical signals to operational decisions. In water-scarcity contexts, complementary measures also matter, including institutional arrangements that support non-conventional resources and demand management. These conditions shape whether technology-enabled insights can translate into sustained allocation and compliance improvements [
10].
Overall, the transition from pilots to durable WRM infrastructure is primarily an institutional design challenge. Technical capability matters, but scale-up ultimately depends on governance arrangements that assign responsibilities, connect information to action, and sustain coordinated implementation over time [
8,
15].
6. Conclusions, Future Directions and Limitations
This review shows that smart technologies can strengthen water resources management in semi-arid Latin America, primarily through improved observability, timeliness, and decision support. Across the reviewed literature, the most consistent evidence concerns operational applications, especially early warning, forecasting, water quality surveillance, and NRW/leakage management. By contrast, evidence on governance-related effects—such as allocation and compliance improvement, institutional coordination, and long-term sustainability—remains more limited, uneven, and less consistently measured.
For Peru and similar semi-arid Latin American settings, the evidence supports a cautious but actionable interpretation. Smart WRM approaches appear promising, but their transfer and scaling should not be assumed to be direct or automatic. Their practical replicability depends on enabling conditions such as interoperable data systems, institutional coordination, financing and O&M capacity, digital skills, and sustained operating conditions. In this sense, the territorial adoption agenda proposed in this paper should be understood as a conditional implementation pathway rather than as a universally transferable template.
Future directions. Future work should prioritize scalable evidence, not additional pilots. Key directions include standardized outcome KPIs, interoperability-ready architectures that integrate RS/GIS, telemetry, and analytics, and reporting of O&M and total cost of ownership, together with measurable allocation/compliance and equity impacts.
Limitations. Findings are constrained by heterogeneous metrics and study designs, which preclude quantitative pooling. Although Scopus, Web of Science, and IEEE Xplore were used, some regional publications may remain underrepresented. Finally, many studies emphasize technical outputs over consistently measured operational and governance outcomes, and the coding scheme may simplify complex hybrid implementations.