{"id":39147,"date":"2026-06-09T09:58:26","date_gmt":"2026-06-09T08:58:26","guid":{"rendered":"https:\/\/www.vtei.cz\/2026\/06\/systemy-zachycovani-destove-vody-a-zvladani-povodnovych-prutoku-ve-venkovskych-oblastech-systematicky-prehled\/"},"modified":"2026-06-09T17:49:27","modified_gmt":"2026-06-09T16:49:27","slug":"systemy-zachycovani-destove-vody-a-zvladani-povodnovych-prutoku-ve-venkovskych-oblastech-systematicky-prehled","status":"publish","type":"post","link":"https:\/\/www.vtei.cz\/en\/2026\/06\/systemy-zachycovani-destove-vody-a-zvladani-povodnovych-prutoku-ve-venkovskych-oblastech-systematicky-prehled\/","title":{"rendered":"Rainwater harvesting systems and flood water management in rural areas: A systematic review"},"content":{"rendered":"<h2 class=\"03NADPIS2\">ABSTRACT<\/h2>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">In\u00a0a\u00a0climate marked by prolonged drought, observed mainly in\u00a0arid and semi-arid areas, the\u00a0installation of\u00a0hydraulic systems for rainwater collection and storage in\u00a0rural and isolated areas is becoming a\u00a0necessity to preserve livestock and ensure water security for the\u00a0local population. For this purpose, this review synthesizes recent studies on the\u00a0various hydraulic systems used for rainwater harvesting (RWH) in\u00a0rural areas to support agriculture, livestock, and households. This review examines 66 relevant studies published in\u00a0journals indexed in\u00a0ScienceDirect and Scopus over a\u00a0period of\u00a0five years (January 2021 \u2013 December 2025). It emphasizes the\u00a0importance of\u00a0design based on the\u00a0specific characteristics of\u00a0each location or country, the\u00a0criteria for selecting implementation sites, the\u00a0impact of\u00a0RWH systems on agriculture, livestock, and rural households, existing challenges, and proposes some guidelines for sustainable rainwater management and flood reduction.<\/span><\/p>\n<h2 class=\"03NADPIS2\">INTRODUCTION<\/h2>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">Pressure on water and natural resources in\u00a0the\u00a0world, exacerbated by climate change, is threatening agriculture, livestock and increasing poverty in\u00a0arid and semi-arid areas, especially in\u00a0rural, isolated localities. It is in\u00a0this context that rainwater harvesting (RWH) systems have gained importance internationally as a\u00a0sustainable rainwater management solution.<\/span><\/p>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">RWH is the\u00a0process of\u00a0collecting raindrops or runoff and storing them in\u00a0tanks, reservoirs, or other storage systems. The\u00a0harvested rainwater can\u00a0subsequently be utilized for various on-site purposes due to its limited captured volume. Rainfall can\u00a0be collected from different sources. RWH systems (RWHS) are designed to collect surface runoff from steep and sparsely forested mountain\u00a0slopes to agricultural areas [1]. As a\u00a0result, these systems serve a\u00a0dual purpose: providing water supply and managing floodwater, which makes them both distinctive and exceptional [2]. Okello et al. [3] claimed that in\u00a0addition to increasing the\u00a0availability of\u00a0water, RWH helps restore nearby groundwater sources and generates employment opportunities in\u00a0the\u00a0local communities. Consequently, the\u00a0widespread adoption of\u00a0RWH as a\u00a0strategic solution to water scarcity has contributed to a\u00a0reduction in\u00a0groundwater extraction. RWH has been employed not only to address the\u00a0growing imbalance between water supply and demand but also to promote social, environmental, and economic development, ultimately enhancing the\u00a0quality of\u00a0life in\u00a0arid and semi-arid areas [4\u20137].<\/span><\/p>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">Over the\u00a0past few decades, numerous researchers have shown their interest in\u00a0RWH technologies and practices, and also several countries worldwide have been using RWHS as an\u00a0alternative measure to provide water for domestic and agricultural uses in\u00a0dry and isolated areas. However, these RWHS differ from one location to another according to multiple criteria such as: the\u00a0geographical situation, land configuration, hydrographic network, purpose of\u00a0rainwater usage, socio-economic situation, local population preferences, and environmental contexts. Consequently, researchers try to combine all these criteria to design and implement an\u00a0adapted RWHS for a\u00a0specific location.<\/span><\/p>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">Current review studies primarily focus on the\u00a0benefits of\u00a0RWHS in\u00a0addressing water scarcity in\u00a0drought-prone areas [8, 9], the\u00a0modernization of\u00a0traditional RWHS [10, 11], their potential applications in\u00a0agriculture and livestock activities [12, 13], and the\u00a0integration of\u00a0new technologies to maximize RWHS performance [14, 15]. Nonetheless, these reviews have adopted diverse methodological approaches, and often include sources with varying levels of\u00a0scientific rigor, such as professional reports and book chapters. Furthermore, some focus narrowly on a\u00a0specific aspect of\u00a0RWH or are limited to particular regions, such as the\u00a0Middle East and North Africa (MENA) or low-and middle-income countries (LMICs). This disjointed perspective hampers a\u00a0comprehensive understanding of\u00a0the\u00a0global importance and diverse applications of\u00a0RWHS across multiple sectors. To address these gaps, this study conducts a\u00a0systematic literature review based on the\u00a0Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA) framework, exclusively considering peer-reviewed articles published in\u00a0Scopus and ScienceDirect from January 2021 to December 2025. This structured and transparent methodology enhances reproducibility and offers a\u00a0thorough synthesis of\u00a0worldwide research. Distinct from earlier reviews on RWHS (e.g., [7, 16\u201319]), this study is organized to facilitate understanding of\u00a0the\u00a0complex structure of\u00a0RWHS, directed by crucial questions aimed at identifying the\u00a0scholarly advancements of\u00a0RWH, analyzing different research contributions in\u00a0RWH, and determining the\u00a0challenges of\u00a0rain\u00a0and flood water management policies. Throughout this scholarly pursuit, this study offers a\u00a0detailed synthesis of\u00a0the\u00a0main\u00a0principal RWH techniques, applications, and practices that exist worldwide. It emphasizes recent advancements and future perspectives for sustainable water resources management.<\/span><\/p>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">This paper is organized as follows: The first section presents the methodology of this study, highlighting the criteria used for selecting sources and studies using the PRISMA-based systematic literature review. The second part consists of a literature review that summarizes the results of all the reviewed articles. This section is organized into several parts: first, an overview of historical and traditional RWH techniques in arid and semi-arid areas; followed by a technical\u00a0<\/span><span lang=\"EN-GB\">review of\u00a0RWHS, including types, design considerations, implementation sites, and maintenance practices. The\u00a0next section discusses the\u00a0impacts of\u00a0RWH on agriculture, livestock, and livelihoods in\u00a0rural areas, as well as its role in\u00a0managing food and water erosion. Finally, the\u00a0concluding section examines water management policies and institutional support mechanisms.<\/span><\/p>\n<h2 class=\"03NADPIS2\">METHODS<\/h2>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">To conduct this review, the\u00a0methodology of\u00a0systematic literature review was used to collect, analyze, and evaluate a\u00a0certain\u00a0number of\u00a0scientific papers on RWH in\u00a0the\u00a0world. For this purpose, the\u00a0guidelines of\u00a0the\u00a0PRISMA were employed to guarantee an\u00a0organized and credible selection process. Moher et al. [20] introduced the\u00a0PRISMA statement as a\u00a0set of\u00a0directives aiming to enhance the\u00a0transparency and comprehensiveness of\u00a0reporting in\u00a0systematic reviews through a\u00a0defined set of\u00a0steps, containing article identification, screening, eligibility, and final inclusion.<\/span><\/p>\n<h3 class=\"03NADPIS3\">Eligibility criteria<\/h3>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">RWH has become a\u00a0popular topic since the\u00a0early 2000s, with an\u00a0increase in\u00a0the\u00a0number of\u00a0publications over the\u00a0years [16]. Considering this extensive volume of\u00a0publications, the\u00a0studies included in\u00a0the\u00a0present review were carefully selected according to predefined eligibility criteria to ensure relevance and coherence. These eligibility criteria included peer-reviewed journal articles written in\u00a0English, published between January 2021 and December 2025, indexed in\u00a0Scopus and available in\u00a0ScienceDirect and Scopus, and related to rural RWH.<\/span><\/p>\n<h3 class=\"03NADPIS3\">Search strategy<\/h3>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">The\u00a0bibliographic databases used in\u00a0the\u00a0article search: ScienceDirect and Scopus. Particular keywords and terms related to rural RWH were utilized in\u00a0this search (<span class=\"01ITALIC\">Fig.\u00a01<\/span>). The\u00a0query was structured as follows: (\u201crainwater\u201d OR \u201cstormwater\u201d OR \u201csurface water\u201d) AND (\u201charvesting\u201d OR \u201ccollecting\u201d OR \u201cstoring\u201d OR \u201cmanagement\u201d OR \u201cconservation\u201d OR \u201cwater erosion\u201d) AND (\u201crural\u201d OR \u201cmountain\u201d OR\u00a0\u201carid\u201d OR \u201csemi-arid\u201d OR \u201cdry area\u201d) AND ( \u201cagriculture\u201d OR \u201clivestock\u201d OR \u201cfields\u201d) AND ( \u201ctechniques\u201d OR \u201cdesign\u201d OR \u201chydraulic system\u201d OR \u201cconstruction materials\u201d OR\u00a0\u201cimplementation site\u201d OR \u201cefficiency\u201d). Using this search strategy, an\u00a0initial dataset of\u00a01,854 publications was obtained.<\/span><\/p>\n<h6><a href=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-1-1.jpg\" rel=\"shadowbox[sbpost-39147];player=img;\"><img decoding=\"async\" class=\"alignnone wp-image-39067 size-full lazyload\" data-src=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-1-1.jpg\" alt=\"\" width=\"800\" height=\"438\" data-srcset=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-1-1.jpg 800w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-1-1-300x164.jpg 300w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-1-1-768x420.jpg 768w\" data-sizes=\"(max-width: 800px) 100vw, 800px\" src=\"data:image\/svg+xml;base64,PHN2ZyB3aWR0aD0iMSIgaGVpZ2h0PSIxIiB4bWxucz0iaHR0cDovL3d3dy53My5vcmcvMjAwMC9zdmciPjwvc3ZnPg==\" style=\"--smush-placeholder-width: 800px; --smush-placeholder-aspect-ratio: 800\/438;\" \/><\/a><\/h6>\n<h6>Fig. 1. Strategy used in\u00a0the\u00a0search of\u00a0bibliographic databases<\/h6>\n<h3 class=\"03NADPIS3\">Screening and selection process<\/h3>\n<p class=\"03NADPIS4\"><span style=\"color: #0bb814;\"><strong><span style=\"text-transform: none;\">Management of\u00a0the\u00a0references<\/span><\/strong><\/span><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">All the\u00a0retrieved publications from the\u00a0searches were imported into Zotero, which is a\u00a0reference management software [21] to identify and remove all the\u00a0duplicated publications. At this level, 79 papers were removed from the\u00a0dataset for being duplicates (<em><span class=\"01ITALIC\">Fig.\u00a02<\/span><\/em>).<\/span><\/p>\n<h6><a href=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-2-1.jpg\" rel=\"shadowbox[sbpost-39147];player=img;\"><img decoding=\"async\" class=\"alignnone wp-image-39066 size-full lazyload\" data-src=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-2-1.jpg\" alt=\"\" width=\"800\" height=\"848\" data-srcset=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-2-1.jpg 800w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-2-1-283x300.jpg 283w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-2-1-768x814.jpg 768w\" data-sizes=\"(max-width: 800px) 100vw, 800px\" src=\"data:image\/svg+xml;base64,PHN2ZyB3aWR0aD0iMSIgaGVpZ2h0PSIxIiB4bWxucz0iaHR0cDovL3d3dy53My5vcmcvMjAwMC9zdmciPjwvc3ZnPg==\" style=\"--smush-placeholder-width: 800px; --smush-placeholder-aspect-ratio: 800\/848;\" \/><\/a>Fig. 2. Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA) flow diagram<\/h6>\n<p class=\"03NADPIS4\"><strong><span style=\"text-transform: none; color: #0bb814;\">Selection process<\/span><\/strong><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">After removing all the\u00a0duplicated records, a\u00a0second filter was applied on the\u00a0remaining 1,775 records based on the\u00a0article titles to ensure the\u00a0inclusion of\u00a0relevant content. Accordingly, articles that did not contain\u00a0the\u00a0predefined keywords (<em><span class=\"01ITALIC\">Fig.\u00a01<\/span><\/em>) in\u00a0the\u00a0title were excluded from the\u00a0database. Thus, 1,579 articles were removed, and the\u00a0number of\u00a0records at this stage decreased to 196. To further refine this dataset, a\u00a0third manual filter was applied using the\u00a0article abstracts, aiming to include only articles that align with these three main\u00a0topics:<\/span><\/p>\n<ul>\n<li class=\"01TEXT-ODRAZKY\">RWH practices and technologies in\u00a0agriculture, livestock preservation, and rural households;<\/li>\n<li class=\"01TEXT-ODRAZKY\">Floodwater and water erosion management in\u00a0rural areas;<\/li>\n<li class=\"01TEXT-ODRAZKY\">Water government policy.<\/li>\n<\/ul>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">Both authors conducted this process, and unclear cases were analyzed in\u00a0more detail and discussed until a\u00a0consensus decision was reached.<\/span><\/p>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">At the\u00a0end of\u00a0this process, 96 articles were excluded after reading the\u00a0abstract, and 100 articles were selected for additional analysis (<em><span class=\"01ITALIC\">Fig.\u00a02<\/span><\/em>).<\/span><\/p>\n<p class=\"03NADPIS4\"><span style=\"color: #0bb814;\"><strong><span style=\"text-transform: none;\">Inclusion\/exclusion criteria<\/span><\/strong><\/span><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">After an\u00a0in-depth reading of\u00a0the\u00a0full-text articles meeting the\u00a0initial screening criteria, clear inclusion and exclusion criteria were established to confirm the\u00a0alignment with the\u00a0research main\u00a0themes (<em><span class=\"01ITALIC\">Tab.\u00a01<\/span><\/em>). As a\u00a0result of\u00a0this process, 89 articles were selected for further evaluation. The\u00a0entire screening process was documented using Zotero and Excel spreadsheets, including relevant notes for each article.<\/span><\/p>\n<h5>Tab.\u00a01. Inclusion and exclusion criteria<\/h5>\n<h3><a href=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-tab-1-3.jpg\" rel=\"shadowbox[sbpost-39147];player=img;\"><img decoding=\"async\" class=\"alignnone wp-image-39063 size-full lazyload\" data-src=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-tab-1-3.jpg\" alt=\"\" width=\"800\" height=\"749\" data-srcset=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-tab-1-3.jpg 800w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-tab-1-3-300x281.jpg 300w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-tab-1-3-768x719.jpg 768w\" data-sizes=\"(max-width: 800px) 100vw, 800px\" src=\"data:image\/svg+xml;base64,PHN2ZyB3aWR0aD0iMSIgaGVpZ2h0PSIxIiB4bWxucz0iaHR0cDovL3d3dy53My5vcmcvMjAwMC9zdmciPjwvc3ZnPg==\" style=\"--smush-placeholder-width: 800px; --smush-placeholder-aspect-ratio: 800\/749;\" \/><\/a><\/h3>\n<p class=\"03NADPIS3\"><span style=\"color: #0bb814;\"><strong>Data collection process<\/strong><\/span><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">All data relating to the\u00a089 selected articles were meticulously extracted and organized into an\u00a0Excel spreadsheet. This retrieved dataset includes key information, specifically authors\u2019 names, articles\u2019 titles, years of\u00a0publication, study locations, main\u00a0topics, abstracts, research methodologies, and results. This structured approach simplified the\u00a0analysis and guaranteed easy access to articles details for comparison and review.<\/span><\/p>\n<p class=\"03NADPIS3\"><span style=\"color: #0bb814;\"><strong>Quality assessment<\/strong><\/span><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">The\u00a0methodological quality of\u00a0all the\u00a0included articles was evaluated based on two main\u00a0criteria:<\/span><\/p>\n<ul>\n<li class=\"01TEXT-ODRAZKY\">The\u00a0clarity of\u00a0the\u00a0research methodology;<\/li>\n<li class=\"01TEXT-ODRAZKY\">The\u00a0pertinence and validity of\u00a0results.<\/li>\n<\/ul>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">\u00a0<\/span><span lang=\"EN-GB\">This assessment was conducted manually by both authors, and notes on the\u00a0limitations of\u00a0each article were recorded in\u00a0Excel spreadsheets. According to these specified criteria, 8 articles were excluded due to weak methodology, and 15 articles were excluded due to the\u00a0absence of\u00a0relevance and validity of\u00a0findings. Following this assessment, 66 articles satisfied the\u00a0criteria and were selected for final inclusion.<\/span><\/p>\n<p class=\"03NADPIS3\"><span style=\"color: #0bb814;\"><strong>Bias assessment<\/strong><\/span><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">Following the\u00a0quality assessment, a\u00a0bias assessment was conducted on the\u00a0remaining 66 articles using the\u00a0Critical Appraisal Skills Program (CASP) checklist. This evaluation focused on the\u00a0clarity of\u00a0the\u00a0research process, the\u00a0presence of\u00a0references, empirical data, and the\u00a0validity of\u00a0findings. Unlike the\u00a0previous quality assessment, no articles were excluded at this stage based on bias considerations, indicating that all the\u00a0included studies demonstrated an\u00a0acceptable level of\u00a0bias control and transparency.<\/span><\/p>\n<p class=\"03NADPIS3\"><span style=\"color: #0bb814;\"><strong>Data synthesis<\/strong><\/span><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">The\u00a0definitive dataset containing 66 articles was analyzed using a\u00a0qualitative synthesis approach, enabling the\u00a0identification, organization, and examination of\u00a0each article\u2019s\u00a0findings and results. During this process, outcomes of\u00a0the\u00a0studies were summarized, compared, and heterogeneities were evaluated. Consequently, the\u00a0articles were categorized according to their focus areas into main\u00a0sub-topics, including RWH in\u00a0ancient and modern structures, RWH applications in\u00a0rural settings, floodwater and water erosion management, and water governance policies. This classification provided a\u00a0systematic overview of\u00a0the\u00a0existing literature.<\/span><\/p>\n<p class=\"03NADPIS3\"><span style=\"color: #0bb814;\"><strong>The\u00a0PRISMA flow diagram<\/strong><\/span><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">At the\u00a0conclusion of\u00a0this process, a\u00a0PRISMA flow diagram (<em><span class=\"01ITALIC\">Fig.\u00a02<\/span><\/em>) was constructed manually to illustrate the\u00a0entire selection workflow, starting with the\u00a0initial identification of\u00a0records and ending with the\u00a0final inclusion.<\/span><\/p>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">This structured method ensures transparency and enhances the\u00a0reproducibility of\u00a0the\u00a0review.<\/span><\/p>\n<h2 class=\"03NADPIS2\">RESULTS AND DISCUSSION<\/h2>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">The\u00a0findings synthesize information from the\u00a0selected literature and highlight representative examples from diverse regions. Due to the\u00a0heterogeneity in\u00a0geographical contexts and methodological approaches, the\u00a0strength of\u00a0evidence among the\u00a0reviewed studies is variable, which may influence the\u00a0generalizability of\u00a0the\u00a0conclusions. Consequently, the\u00a0overall confidence in\u00a0the\u00a0body of\u00a0evidence can\u00a0be considered moderate. Therefore, the\u00a0results should be interpreted with caution, taking into account the\u00a0inherent limitations of\u00a0the\u00a0available evidence.<\/span><\/p>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">To facilitate a\u00a0comprehensive analysis, the\u00a0articles from the\u00a0final inclusion were classified and organized into five sub-topics using Zotero:<\/span><\/p>\n<ul>\n<li class=\"01TEXT-ODRAZKY\">historical and traditional RWH techniques in\u00a0arid and semi-arid regions;<\/li>\n<li class=\"01TEXT-ODRAZKY\">main\u00a0characteristics of\u00a0RWHS;<\/li>\n<li class=\"01TEXT-ODRAZKY\">impact of\u00a0RWHS on agriculture, livestock, and life in\u00a0rural households;<\/li>\n<li class=\"01TEXT-ODRAZKY\">floodwater and erosion management in\u00a0rural areas;<\/li>\n<li class=\"01TEXT-ODRAZKY\">water government policy related to RWH and floodwater management.<\/li>\n<\/ul>\n<h3 class=\"03NADPIS3\">Historical and traditional RWH techniques in\u00a0arid and\u00a0semi-arid regions<\/h3>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">RWH has long served as a\u00a0foundation stone of\u00a0water management in\u00a0arid and semi-arid regions, reflecting the\u00a0cleverness and cultural resilience of\u00a0communities challenging water scarcity. This part synthesizes recent studies that collectively highlight the\u00a0importance and the\u00a0diversity of\u00a0these traditional RWH practices and their cultural significance across the\u00a0Middle East, Asia, North Africa, and Sub-Saharan\u00a0Africa.<\/span><\/p>\n<p class=\"03NADPIS4\"><span style=\"color: #0bb814;\"><strong><span style=\"text-transform: none;\">Subterranean\u00a0channels<\/span><\/strong><\/span><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">Subterranean\u00a0channel is one of\u00a0the\u00a0most advanced traditional RWH practices in\u00a0the\u00a0MENA region, designed in\u00a0a\u00a0way to reduce evaporation and increase efficiency. These underground water systems present differences from one country to another in\u00a0techniques and nomenclature: qanats, falaj or aflaj, or foggaras [5]. These systems use gravity to transport water from higher elevation aquifers to lower elevation farmlands. This technique not only provides water to areas with limited surface water accessibility but also reduces water evaporation. On the\u00a0other hand, Weerahewa et al. [22] introduced aflaj as a\u00a0hydraulic system inspired by local traditions and Islamic principles of\u00a0equity insuring fair water distribution in\u00a0the\u00a0Arabian\u00a0Peninsula.<\/span><\/p>\n<p>&nbsp;<\/p>\n<h6><a href=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-3-1.jpg\" rel=\"shadowbox[sbpost-39147];player=img;\"><img decoding=\"async\" class=\"alignnone wp-image-39065 size-full lazyload\" data-src=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-3-1.jpg\" alt=\"\" width=\"800\" height=\"379\" data-srcset=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-3-1.jpg 800w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-3-1-300x142.jpg 300w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-3-1-768x364.jpg 768w\" data-sizes=\"(max-width: 800px) 100vw, 800px\" src=\"data:image\/svg+xml;base64,PHN2ZyB3aWR0aD0iMSIgaGVpZ2h0PSIxIiB4bWxucz0iaHR0cDovL3d3dy53My5vcmcvMjAwMC9zdmciPjwvc3ZnPg==\" style=\"--smush-placeholder-width: 800px; --smush-placeholder-aspect-ratio: 800\/379;\" \/><\/a>Fig. 3. Cross-section of\u00a0qanat system (source: [5])<\/h6>\n<p class=\"03NADPIS4\"><span style=\"color: #0bb814;\"><strong><span style=\"text-transform: none;\">Cisterns<\/span><\/strong><\/span><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">These water storage systems permit water harvesting in\u00a0wet seasons to provide water during the\u00a0prolonged periods of\u00a0drought. Cisterns vary from one location to another, given their typology, construction materials, and they can\u00a0also be open reservoirs, as observed in\u00a0Sela in\u00a0the\u00a0Southern Transjordan\u00a0Plateau [23] or underground like <span class=\"01BOLD\">sarn\u0131\u00e7, <\/span>known as traditional cisterns implanted in\u00a0Bozcaada (T\u00fcrkiye) to ensure water scarcity in\u00a0this island [24].<\/span><\/p>\n<a href=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-4.jpg\" rel=\"shadowbox[sbpost-39147];player=img;\"><img decoding=\"async\" class=\"alignnone wp-image-38855 size-full lazyload\" data-src=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-4.jpg\" alt=\"\" width=\"800\" height=\"1199\" data-srcset=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-4.jpg 800w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-4-200x300.jpg 200w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-4-683x1024.jpg 683w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-4-768x1151.jpg 768w\" data-sizes=\"(max-width: 800px) 100vw, 800px\" src=\"data:image\/svg+xml;base64,PHN2ZyB3aWR0aD0iMSIgaGVpZ2h0PSIxIiB4bWxucz0iaHR0cDovL3d3dy53My5vcmcvMjAwMC9zdmciPjwvc3ZnPg==\" style=\"--smush-placeholder-width: 800px; --smush-placeholder-aspect-ratio: 800\/1199;\" \/><\/a>\n<h6>Fig. 4. Ancient Cistern in\u00a0central Morocco (source: authors)<\/h6>\n<p class=\"03NADPIS4\"><strong><span style=\"text-transform: none; color: #0bb814;\">Surface water harvesting traditional techniques<\/span><\/strong><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">Surface water harvesting can\u00a0also refer to RWH and floodwater harvesting. This method is based on collecting and storing rainwater or floodwater in\u00a0soil, natural reservoirs, or underground for later use. According to Ben Hassen et al. [5], this ancient technique is largely practiced in\u00a0many arid and semi-arid regions around the\u00a0world:<\/span><\/p>\n<ul>\n<li class=\"01TEXT-ODRAZKY\">In\u00a0Tunisia, <span class=\"01BOLD\"><strong>jessour<\/strong> <\/span>are utilized as traditional water collection structures made of\u00a0earthen small dams installed across valley floors to catch rainwater. The\u00a0main\u00a0role of\u00a0jessour is to harvest rainwater from rare events and to transfer it through a\u00a0terracing system, facilitating the\u00a0cultivation of\u00a0crops like olive and almond trees in\u00a0dry environments.<\/li>\n<\/ul>\n<p><em> <a href=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-5.jpg\" rel=\"shadowbox[sbpost-39147];player=img;\"><img decoding=\"async\" class=\"alignnone wp-image-38854 size-full lazyload\" data-src=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-5.jpg\" alt=\"\" width=\"800\" height=\"288\" data-srcset=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-5.jpg 800w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-5-300x108.jpg 300w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-5-768x276.jpg 768w\" data-sizes=\"(max-width: 800px) 100vw, 800px\" src=\"data:image\/svg+xml;base64,PHN2ZyB3aWR0aD0iMSIgaGVpZ2h0PSIxIiB4bWxucz0iaHR0cDovL3d3dy53My5vcmcvMjAwMC9zdmciPjwvc3ZnPg==\" style=\"--smush-placeholder-width: 800px; --smush-placeholder-aspect-ratio: 800\/288;\" \/><\/a><\/em><\/p>\n<h6>Fig. 5. The\u00a0jessour system in\u00a0Tunisia (source: [5])<\/h6>\n<ul>\n<li>\n<p class=\"01TEXT-ODRAZKY\">In\u00a0Yemen, <span class=\"01BOLD\">spate irrigation (e.g., <strong>Wadis<\/strong>)<\/span> is commonly used as an\u00a0ancient and traditional water management method. It is designed using earthen structures to redirect floodwaters by gravity from mountainous catchments to\u00a0agricultural fields to rapidly irrigate them [5].<\/p>\n<\/li>\n<\/ul>\n<h6><a href=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-6.jpg\" rel=\"shadowbox[sbpost-39147];player=img;\"><img decoding=\"async\" class=\"alignnone wp-image-38853 size-full lazyload\" data-src=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-6.jpg\" alt=\"\" width=\"800\" height=\"285\" data-srcset=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-6.jpg 800w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-6-300x107.jpg 300w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-obr-6-768x274.jpg 768w\" data-sizes=\"(max-width: 800px) 100vw, 800px\" src=\"data:image\/svg+xml;base64,PHN2ZyB3aWR0aD0iMSIgaGVpZ2h0PSIxIiB4bWxucz0iaHR0cDovL3d3dy53My5vcmcvMjAwMC9zdmciPjwvc3ZnPg==\" style=\"--smush-placeholder-width: 800px; --smush-placeholder-aspect-ratio: 800\/285;\" \/><\/a><\/h6>\n<h6>Fig. 6. Spate irrigation system in\u00a0Yemen (source: [5])<\/h6>\n<ul>\n<li>\n<p class=\"01TEXT-ODRAZKY\">In\u00a0Kenya and Tanzania, <strong><span class=\"01BOLD\">sand dams<\/span><\/strong> are used to store rainwater in\u00a0sand in\u00a0wet seasons to reduce evaporation and to increase groundwater recharge [3].<\/p>\n<\/li>\n<\/ul>\n<h6><a href=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-7-1.jpg\" rel=\"shadowbox[sbpost-39147];player=img;\"><img decoding=\"async\" class=\"alignnone wp-image-39064 size-full lazyload\" data-src=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-7-1.jpg\" alt=\"\" width=\"800\" height=\"297\" data-srcset=\"https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-7-1.jpg 800w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-7-1-300x111.jpg 300w, https:\/\/www.vtei.cz\/wp-content\/uploads\/2026\/06\/Belkaf-fig-7-1-768x285.jpg 768w\" data-sizes=\"(max-width: 800px) 100vw, 800px\" src=\"data:image\/svg+xml;base64,PHN2ZyB3aWR0aD0iMSIgaGVpZ2h0PSIxIiB4bWxucz0iaHR0cDovL3d3dy53My5vcmcvMjAwMC9zdmciPjwvc3ZnPg==\" style=\"--smush-placeholder-width: 800px; --smush-placeholder-aspect-ratio: 800\/297;\" \/><\/a><\/h6>\n<h6>Fig. 7. Cross-section of\u00a0a\u00a0sand dam system (source: authors)<\/h6>\n<h3 class=\"03NADPIS3\">Main\u00a0characteristics of\u00a0RWHS: innovation, design, implementation, and sustainability<\/h3>\n<p class=\"03NADPIS4\" style=\"margin-top: 0cm;\"><span style=\"color: #0bb814;\"><strong><span style=\"text-transform: none;\">Modernization of\u00a0traditional RWHS<\/span><\/strong><\/span><\/p>\n<p class=\"00TEXTbezodsazenienglish\"><span lang=\"EN-GB\">RWHS have been used for centuries to manage water resources, demonstrating the\u00a0ingenuity and wisdom of\u00a0rural ancient populations. Based on this, contemporary researchers are increasingly interested in\u00a0modernizing traditional RWHS by integrating new technologies and advancements to develop sustainable solutions for water deficiency.<\/span><\/p>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">Although the\u00a0European\u00a0approach considers rainwater as wastewater, Madomguia et al. [11] underscore that rainwater is a\u00a0sustainable water resource, distinct from surface or underground water. A\u00a0recent study by Madomguia et al. [11] highlights the\u00a0important role of\u00a0RWH in\u00a0the\u00a0Mandra Mountains of\u00a0Cameroon. In\u00a0this region, ancient RWHS called the\u00a0<strong><span class=\"01BOLD\">biefs<\/span> are<\/strong> revitalized by residents to serve as small dams. Additionally, stone terraced systems are maintained through the\u00a0implementation of\u00a0green bamboo walls. These methods not only enhance crop yields in\u00a0terrace farming but also help to mitigate flood risks and provide food and water security in\u00a0this mountainous area.<\/span><\/p>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">Similarly, Carrion-Mero et al. [25] emphasize the\u00a0use of\u00a0hydrogeological and geomorphological analysis through Geographic Information Systems (GIS) to more effectively identify hydraulic structures and drainage areas on the\u00a0slopes of\u00a0the\u00a0Chimborazo Volcano in\u00a0Ecuador. The\u00a0research advocates for the\u00a0modernization of\u00a0the\u00a0traditional RWHS \u201c<strong><span class=\"01BOLD\">Camellones<\/span><\/strong>\u201d to increase its efficiency and promote sustainable water management.<\/span><\/p>\n<p class=\"00TEXTenglish\"><span lang=\"EN-GB\">In\u00a0Tunisia, the\u00a0<strong><span class=\"01BOLD\">tabias<\/span><\/strong> system serves as an\u00a0indigenous RWH structure to control flooding. These hydraulic systems consist of\u00a0stone barriers integrated into terraced farms (e.g., jessour) to catch runoff in\u00a0order to safeguard farms from flooding and to provide irrigation water. Considering its vital role in\u00a0agriculture and flood management, the\u00a0Tunisian\u00a0government demolished many traditional tabias and reconstructed a\u00a0significant number of\u00a0these structures using modern construction tools and techniques [10].<\/span><\/p>\n<p><span style=\"color: #0bb814;\"><strong>RWHS types, designs, and suitable sites determination<\/strong><\/span><\/p>\n<p>RWHS are characterized by their variety of\u00a0types and designs according to their geographical locations, hydrological conditions, socio-cultural environment of\u00a0users, and their purposes of\u00a0use. Consequently, numerous studies have been conducted in\u00a0recent years to investigate these systems and to accurately determine their optimal future sites.<\/p>\n<ul>\n<li><strong>Suitable site selection methods<\/strong>: Selecting appropriate sites for implementing RWHS is a\u00a0crucial step to ensure long-term sustainability and efficiency of\u00a0these hydraulic structures [26]. The\u00a0process of\u00a0potential site selection typically involves the\u00a0following steps:<\/li>\n<li><strong>Study area identification and data collection<\/strong>: Define the\u00a0study area, and gather relevant spatial and non-spatial datasets, including topographical maps, geological and hydrological data, meteorological records, Landsat 8 remote sensing (RS) imagery, and socio-economic data [4, 27\u201330].<\/li>\n<li><strong>Criteria identification and data processing<\/strong>: Determine key criteria based on literature review, field experiences, and the\u00a0harvested water potential usage. The\u00a0collected data and criteria are processed and transformed into thematic layers within\u00a0GIS. Common layers include slope, stream order, drainage density, rainfall, soil type, land use\/land cover (LULC), and road networks. These thematic layers are reclassified [26, 28] and standardized using fuzzy membership functions for numerical data and step-wise functions for categorical data [29]. The\u00a0processed layers serve as GIS inputs for generating a\u00a0final suitability map.<\/li>\n<li><strong>Hydrological modeling<\/strong>: To refine the site suitability map, hydrological models such as the Soil and Water Assessment Tool (SWAT) model [27]or the Soil Conservation Service Curve Number (SCS-CN) method [28, 29] can be employed to simulate runoff, infiltration, and sediment yield. Although hydrological modeling is recommended by many researchers, it remains optional to determine the suitable implementation sites for RWHS.<\/li>\n<li><strong>Criteria weighting and Multi-Criteria Decision Analysis (MCDA)<\/strong>: Assign weights to each criteria using methods such as the\u00a0Analytic Hierarchy Process (AHP) [27] or fuzzy AHP [29]. To enhance robustness of\u00a0results, some studies incorporate MCDA techniques combined with statistical analysis of\u00a0spatial associations like Weight of\u00a0Evidence (WOE) [28] or employ the\u00a0VIseKriterijumska Optimizacija (VIKOR) method to rank alternatives based on subjective decisions of\u00a0field experts [29].<\/li>\n<li><strong>Suitability map generation and visualization<\/strong>: Integrate weighted criteria within\u00a0GIS to produce a\u00a0suitability map, classifying the\u00a0study area into categories such as very high, high, moderate, low, and very low suitability<br \/>\n[1, 4, 9, 27\u201329, 31, 32].<\/li>\n<li><strong>Validation and policy alignment<\/strong>: Validate the\u00a0suitability results by linking them to Sustainable Development Goals (SDGs) and examining their alignment with local governmental policies in\u00a0the\u00a0study area [27, 29]. Various modeling tools have been employed to develop RWH suitability maps. These\u00a0include a\u00a0GIS-based SWAT model for assessing the\u00a0sub-daily hydrological influence of\u00a0RWH on landscape irrigation [33]; GIS-based AHP; machine learning algorithms [28]; and a\u00a0Markov chain\u00a0model estimating the\u00a0transition probabilities between hydrological states to optimize RWH site selection [34]. Collectively, these tools aim to assist policymakers and stakeholders in\u00a0establishing sustainable water management frameworks.<\/li>\n<li><strong>RWH types and their design approaches<\/strong>: RWHS exhibit a\u00a0wide variety of\u00a0designs, shaped by their implementation in\u00a0different, diverse cultural and spatial contexts. The\u00a0table below (Tab.\u00a02), compiled from a\u00a0review of\u00a0numerous studies published globally between 2021 and 2025, summarizes the\u00a0design approaches associated with each existing RWH type. Notably, innovative RWH structures and methods are primarily developed in\u00a0China, such as Bioinspired one-dimensional (1D) structures [15] and road-based RWH technologies [35,\u00a036]. Conversely, recent research in\u00a0India emphasizes RWHS that prioritize minimal water contamination, exemplified by designs like the\u00a0rain\u00a0saucer [37].<\/li>\n<\/ul>\n<p>In\u00a0arid and semi-arid rural regions in\u00a0Pakistan, Sri Lanka, and Djibouti, traditional RWHS such as ponds, percolation tanks, and small tanks are common. These structures serve as small water surface reservoirs for local uses like irrigation and livestock watering, and they also facilitate groundwater recharge. Their designs are generally simple, reflecting the\u00a0low construction material requirements. These RWHS are typically located on gentle slopes, generally less than\u00a05\u00a0%, with soil conditions tailored to their function: clayey or loamy soils for ponds to minimize seepage, and permeable soils like sandy or fractured rock formations for percolation tanks to allow water infiltration into the\u00a0aquifers, ensuring groundwater recharge [28, 29]. Small tanks are often interconnected in\u00a0cascade systems to maximize water distribution and reduce evaporation losses [32].<\/p>\n<p>In\u00a0Middle Eastern countries, dams and check dams are considered the\u00a0ultimate solutions to water scarcity. Their design and construction are heavily influenced by local site conditions, particularly local geology and hydrology, to determine optimal shape, storage capacity, and construction materials, which are typically locally sourced, like gravel, clay, and limestone rocks; to reduce construction costs and enhance durability. The\u00a0primary purpose of\u00a0these structures also guides their design; check dams are mainly intended for erosion control and RWH, whereas dams serve multiple functions, including flood management, water storage for agricultural, domestic, and industrial use, and power generators [1, 4, 9, 27, 28, 31].<\/p>\n<p>These integrated design methods, combining traditional approaches with modern modeling tools, assist policymakers and investors in\u00a0identifying appropriate locations for RWHS installation and selecting suitable RWH designs for each site, thereby improving the\u00a0effectiveness and sustainability of\u00a0RWH ingenuities [28, 29, 32].<\/p>\n<p>Additionally, Membrane technologies were introduced as a\u00a0complement to RWHS. They are generally installed downstream of\u00a0the\u00a0RWH structures as a\u00a0rainwater treatment to ensure water quality before its reuse for domestic and agricultural purposes. This method consists of\u00a0filtering rainwater using different types of\u00a0membranes (surface membrane, gravity-driven membrane processes, and membrane bio-reactor process) [14].<\/p>\n<h3>Considerations for maintenance and sustainability<\/h3>\n<p>The\u00a0durability of\u00a0RWHS is highly desirable, especially given their positive impacts on multiple levels. Sustainability in\u00a0RWH concerns the\u00a0following aspects:<\/p>\n<ul>\n<li><strong>Full and lasting engagement of\u00a0all actors<\/strong><br \/>\nThe\u00a0success of\u00a0a\u00a0RWH project ultimately depends on the\u00a0commitment of\u00a0all water sector actors, including government agencies, investors, farmers, and the\u00a0rural population as a\u00a0whole. This collaboration would simplify the\u00a0construction, preservation, and maintenance operations of\u00a0RWH structures [38]. These contributors are instrumental in\u00a0bringing the\u00a0project to life, from its inception to installation and operationalization. In\u00a0addition, Pala et al. [18] emphasize the\u00a0importance of\u00a0education and awareness among rural communities regarding RWHS conservation and advocate for the\u00a0enforcement of\u00a0laws and amendments to preserve these hydraulic structures.<\/li>\n<li><strong>Maintenance of\u00a0the\u00a0RWH structures<\/strong><br \/>\nGiven the\u00a0high initial costs of\u00a0modern RWH structures, their maintenance expenses and considerations during the\u00a0operational phase should be factored in\u00a0from the\u00a0feasibility and conceptual stages to ensure their long-term durability [7, 39]. Regular maintenance is crucial to ensure the\u00a0longevity of\u00a0RWHS [40]. This includes cleaning water storage tanks, ponds, cisterns, and catchment areas; monitoring odor, color, and chemical qualities of\u00a0stored water; treating stagnant water before use; and repairing the\u00a0defective parts of\u00a0the\u00a0RWHS [17]. Adequate and periodic maintenance helps preserve the\u00a0functionality of\u00a0the\u00a0structures and ensures the\u00a0continuity of\u00a0their positive impacts.<\/li>\n<li><strong>Environmental sustainability<\/strong><br \/>\nRWH projects have demonstrated positive environmental impacts by contributing to reducing energy consumption, recharging groundwater, mitigating floods, and thereby restoring some aspects of\u00a0the\u00a0natural water cycle [19]. This involves encouraging the\u00a0sustainable use of\u00a0water resources and preserving local ecosystems.<\/li>\n<li><strong>Socio-economic and environmental assessment of\u00a0RWHS<\/strong><br \/>\nWhile the\u00a0fundamental principle of\u00a0the\u00a0RWH technique is simple: collecting, storing, and providing water, the\u00a0selection of\u00a0suitable RWHS implementation sites remains a\u00a0challenging decision for researchers and decision-makers, as it depends on socio-economic and environmental parameters.<\/li>\n<\/ul>\n<p>Socio-economic hardships are the\u00a0main\u00a0challenges for indigenous peoples in\u00a0affording water or investing in\u00a0water structures [6]. Therefore, RWHS offer deprived communities indisputable social and economic benefits [41]. Accordingly, Rodrigues de S\u00e1 Silva et al. [7] emphasize the\u00a0positive socio-economic impacts of\u00a0using RWHS in\u00a0agriculture and households in\u00a0arid and semi-arid regions on the\u00a0Loess Plateau in\u00a0China, noting an\u00a0annual water saving of\u00a075.8\u00a0m3 per household and an\u00a0annual energy saving of\u00a0138.6 kWh per household. A\u00a0similar study conducted by Richards et al. [42] in\u00a0India found that installing RWHS in\u00a0rural public schools could save about 25\u00a0% of\u00a0the\u00a0water used for non-drinking purposes. Additionally, Khanal et al. [43] underscore the\u00a0importance of\u00a0RWH users\u2019 awareness of\u00a0sustainable water management practices and recommend integrating rainwater-related courses into university programs to expand knowledge in\u00a0this field. However, Xue et al. [44] point out that the\u00a0economic advantages of\u00a0RWH and utilization differ considerably depending on the\u00a0climatic conditions of\u00a0a\u00a0region.<\/p>\n<p>Socio-environmental variables such as topographical, climatological, hydrological, agricultural, geological, pedological, and human\u00a0factors are essential in\u00a0successfully selecting RWHS potential sites on large-scale regions [45]. In\u00a0this context, Teston et al. [19] proposed an\u00a0analysis of\u00a0the\u00a0prospective location of\u00a0RWHS that considers environmental impacts generated by such systems using Life Cycle Assessment (LCA) and water balance modeling tools.<\/p>\n<h2>RWHS USED TO IMPROVE THE QUALITY OF AGRICULTURE, LIVESTOCK, AND LIFE IN RURAL HOUSEHOLD<\/h2>\n<h3>Impact of\u00a0RWH on agriculture in\u00a0rural areas<\/h3>\n<p>Rural agriculture is menaced by water scarcity that is due to climate change and over-extraction of\u00a0groundwater [13]. This situation is exacerbated by irregular precipitation patterns and inefficient irrigation structures, particularly in\u00a0arid and semi-arid regions. To mitigate this issue, RWH appeared as the\u00a0eventual solution to increase water efficiency and enhance the\u00a0resilience of\u00a0rural agricultural systems. RWH is crucial for ensuring adequate water for crop production, which enhances rural economics [12, 30]. In\u00a0the\u00a0following, concrete examples of\u00a0RWH benefits on crop yields were identified based on the\u00a0reviewed articles.<\/p>\n<p>In\u00a0arid and semi-arid regions of\u00a0China, several studies were led on the\u00a0cultivation of\u00a0alfalfa in\u00a0ridge-furrow RWH in\u00a0combination with biochar by Wang\u00a0et\u00a0al.\u00a0[46] and with chopped straw by Zhao et al. [47]. These studies demonstrated a\u00a0significant positive impact on crop productivity and an\u00a0optimized water supply. Consequently, this proves the\u00a0resilience of\u00a0high-value crops to drought. Similarly, Chen et al. [48] highlighted the\u00a0meaningful increase of\u00a0maize yields in\u00a0farms relying on ridge-furrow RWHS, which enhances livelihoods of\u00a0local farmers.<\/p>\n<p>In\u00a0marginal areas of\u00a0Zimbabwe, a\u00a0recent study conducted by Kubiku et\u00a0al.\u00a0[49] on two varieties of\u00a0sorghum as the\u00a0main\u00a0food crop in\u00a0Southern Africa showed that field-edge RWHS are promising low-cost water and nutrient management in\u00a0sorghum\u2019s\u00a0rainfed farms, boosting crop productivity and enhancing food security.<\/p>\n<p>In\u00a0Turkey\u2019s\u00a0semi-humid Black Sea region, Yildirim et al. [50] led research on the\u00a0effects of\u00a0ridge-furrow RWHS on the\u00a0growth, yield, and quality of\u00a0red pepper. The\u00a0findings indicate that RWHS improved red pepper production and contributed to the\u00a0achievement of\u00a0sustainable red pepper net income for farmers in\u00a0the\u00a0region.<\/p>\n<p>In\u00a0arid degraded areas of\u00a0Jordan, two RWHS (the\u00a0Vallerani and the\u00a0Marab) were implanted in\u00a0the\u00a0Badia region to collect rainwater and support vegetation growth. The\u00a0study emphasizes the\u00a0important role of\u00a0RWHS in\u00a0enhancing land rehabilitation and sustainable agriculture [51].<\/p>\n<p>In\u00a0India, [52] recommended using RWH in\u00a0on-farm reservoirs as a\u00a0strategic approach to increase second-crop yields and improve water management in\u00a0small-scale farming communities.<\/p>\n<h3>Impact of\u00a0RWH on livestock and the\u00a0quality of\u00a0their products<\/h3>\n<p>Water scarcity highly impacts livestock productivity, particularly in\u00a0dryland regions where the\u00a0water shortage is a\u00a0main\u00a0stressor for cattle. In\u00a0fact, animals facing water stress often conserve their body water by decreasing feed intake, which negatively affects their health, reproductive performance, growth rates, and product quality [53]. Therefore, sheep are directly affected by water restrictions, losing between 1.2 and 21.5\u00a0% of\u00a0their body weight, as confirmed by Chikwanha et al. [53], influencing meat quality and quantity. Likewise, Halimani et\u00a0al.\u00a0[54] found that smallholder sheep farmers in\u00a0South Africa\u2019s\u00a0arid areas notice water deficiency as a\u00a0major risk, pushing them to implement various water management strategies (e.g., RWHS) to alleviate stress on their livestock.<\/p>\n<p>RWH installations become a\u00a0necessity in\u00a0arid and semi-arid areas to enhance cattle\u2019s\u00a0quality by offering additional water supply during dry periods. According to Chikwanha et al. [53] and Halimani et al. [54] access to RWH has a\u00a0positive impact on livestock productivity and, consequently, on smallholder sheep farmers by enhancing water security and being able to maintain\u00a0production levels even in\u00a0drought periods. RWHS allows farmers, particularly underground groups, to invest in\u00a0supplementary feeding and use adapted breeds to improve animals\u2019 growth, health, and meat quality. Meanwhile, Muhirirwe et al. [55] emphasize the\u00a0importance of\u00a0RWHS on dairy production, increasing milk yield and quality by reducing dependency on seasonal water sources and supporting livestock survival. Thus, RWHS guarantee consistent water supply for both animals and crop cultivation, thereby enhancing the\u00a0nutritional and economic value of\u00a0livestock products.<\/p>\n<h3>RWH and the\u00a0quality of\u00a0life in\u00a0rural households<\/h3>\n<p>RWH has shown a\u00a0significant contributionin\u00a0converting rural households by mitigating water scarcity, boosting agricultural productivity, and enhancing livelihood resilience in\u00a0water-scarce regions. From this perspective, a\u00a0recent study by Waqas et al. [40] revealed that the\u00a0use of\u00a0RWH structures to offer additional irrigation in\u00a0fields increased the\u00a0food security in\u00a0Potohar Plateau (Pakistan). Similarly, Gebru et al. [56] highlight the\u00a0crucial role of\u00a0RWH technologies in\u00a0guaranteeing food security for households in\u00a0Ethiopia\u2019s\u00a0arid and semi-arid regions. These technologies allow the\u00a0use of\u00a0rainwater to cultivate crops during dry seasons and help diversify agricultural production.<\/p>\n<p>In\u00a0localities where households are exposed to flooding and poor drainages like in\u00a0Asuncion (Paraguay), RWHS is considered an\u00a0ultimate solution for managing the\u00a0risks associated with this natural phenomenon [57].<\/p>\n<p>Domestic clean\u00a0water supply in\u00a0rural arid and semi-arid areas is gradually being provided by RHWS. Garc\u00eda-Avila et al. [17] reviewed RWH and storing systems and their potential to offer safe drinkable water in\u00a0rural households, and emphasized the\u00a0importance of\u00a0monitoring the\u00a0stored water quality parameters, such as pH, turbidity, and E. coli, to protect public health. In\u00a0another study, Osayemwenre &amp; Osibote [58] provided an\u00a0overview of\u00a0the\u00a0health hazards related to RWH from various rooftops (e.g., green, conventional, and photovoltaic rooftops). The\u00a0research identified potential contaminants like microbes and heavy metals, which may negatively affect the\u00a0rural population\u2019s\u00a0health if they are not properly managed. Therefore, Garc\u00eda-Avila et al. [17] highlighted the\u00a0major role of\u00a0careful selection of\u00a0materials, regular disinfestation, and maintenance of\u00a0RWHS to ensure the\u00a0safe use of\u00a0these systems.<\/p>\n<p>Despite its benefits for agriculture, livestock, and life in\u00a0rural households, the\u00a0adaptation of\u00a0RWHS faces numerous challenges. Muhirirwe et\u00a0al.\u00a0[55] noticed the\u00a0prohibitive initial cost of\u00a0RWH innovative structures, although its long-term advantages. Also, Chikwanha et al. [53] and Halimani et\u00a0al.\u00a0[54] pointed out that the\u00a0main\u00a0obstacles to RWHS installation by small-scale farmers are the\u00a0limited resources, lack of\u00a0technical knowledge, and insufficient policy support.<\/p>\n<h2>FLOODWATER AND EROSION MANAGEMENT IN RURAL AREAS<\/h2>\n<h3>RWH and water erosion management<\/h3>\n<p>Water erosion is considered the main threat to agricultural lands around the globe. It affects the sustainability of agricultural farms and grazing areas. According to Firoozi &amp; Firoozi [59], water erosion occurs through hydrodynamic forces, where rainwater flows or infiltrates through the soil, thereby removing and transporting soil particles. This process gradually alters the landscape and leads to the loss of cultivable land. To control water erosion Yu et al. [60] insist on studying precipitation regimes because rainfall intensity is considered the primary factor of soil detachment. Therefore, Haddad et al. [61] present RWH as an eventual solution to collect and store runoff, reducing erosion\u00a0effects and supporting the\u00a0growth of\u00a0local plants in\u00a0the\u00a0rangeland of\u00a0Jordan. Analogously, RWH by tied ridges slows down the\u00a0erosive runoff during extreme rainfall events and harvests water during light rainfall events in\u00a0Tanzania [62].<\/p>\n<h3>RWH and flood water management<\/h3>\n<p>Following the\u00a0climate changes marked by consecutive drought years, irregular precipitation, and unpredictable flood events, the\u00a0sustainable management of\u00a0these risks has become increasingly essential, particularly in\u00a0arid and semi-arid regions. In\u00a0this context, RWH appears as a\u00a0dual solution to mitigate flood impacts while storing overflowing water for reuse in\u00a0rural activities such as crop irrigation, livestock watering, and domestic use. Ansari et al. [63] provide a\u00a0concrete example of\u00a0the\u00a0positive impact of\u00a0implementing RWH structures in\u00a0Pakistan, specifically the\u00a0Mangla Dam. Since its commissioning, the\u00a0dam has been able to reduce the\u00a0intensity of\u00a0flooding in\u00a0the\u00a0Upper Jhelum Basin\u00a0by 20\u00a0%, despite its primary objectives being water storage for irrigation and power generation. Similarly, Raoufi &amp; Tsubaki [2] propose an\u00a0innovative RWHS that transforms floods into a\u00a0mitigating solution for drought in\u00a0the\u00a0Southwestern provinces of\u00a0Iran. This approach involves renovating traditional RWHS (e.g., qanat, Ab-Anbar) to effectively manage and store excess floodwater for use during drought periods. Meanwhile, farmers in\u00a0the\u00a0Jordanian\u00a0desert use floodwater to support agriculture through a\u00a0method known as \u201cfloodwater farming\u201d. This technique relies on ancient RWHS like wall-and-channel networks to introduce, alleviate, store, and irrigate crops with floodwater [64]. In\u00a0the\u00a0same vein, Ndayiragije et al. [39] highlight the\u00a0important role of\u00a0floodwater harvesting and reuse in\u00a0promoting socio-economic development. This practice significantly reduces the\u00a0energy required for pumping underground water while providing sustainable water for agricultural activities.<\/p>\n<p>Overall, the\u00a0reviewed studies demonstrate that RWH functions as an\u00a0effective land and water management strategy, simultaneously mitigating erosion and reducing flood risks. RWHS enhance water infiltration and help protect agricultural land from degradation. Furthermore, the\u00a0harvested floodwater can\u00a0be used for non-potable purposes such as irrigation and livestock activities, thereby strengthening resilience in\u00a0arid and semi-arid regions. Collectively, the\u00a0literature advocates for the\u00a0adoption of\u00a0RWH techniques to promote sustainable agriculture and improve rural livelihoods.<\/p>\n<h3>Water government policy related to RWH and floodwater management<\/h3>\n<p>Given the\u00a0current global situation marked by successive drought years and irregular rainfall patterns, especially in\u00a0arid and semi-arid regions, exacerbated by phenomena such as water erosion and flooding, integrating RWH in\u00a0its diverse forms into water resource management policies has become an\u00a0obligation for countries. This integration aims to ensure sustainable water management in\u00a0agriculture and to better handle risks related to water erosion and floods.<\/p>\n<p>Saudi Arabia suffers from severe water scarcity due to high evaporation and low rainfall, and the\u00a0significant water use in\u00a0agriculture (87\u00a0% of\u00a0the\u00a0kingdom\u2019s\u00a0water). Consequently, the\u00a0Saudi Arabian\u00a0government has been prompted to adopt advanced strategies in\u00a0the\u00a0agricultural sector, such as integrating precision irrigation, encouraging less water-intensive crops, and enhancing RWH structures and fog water collection [65]. In\u00a0the\u00a0same vein, Egypt is affected by serious water scarcity problems like flash floods and the\u00a0salinization of\u00a0groundwater. These challenges highlight the\u00a0necessity of\u00a0identifying suitable RWH sites and combining this technology with hydrological modeling to decrease flash flood risks and enhance aquifer recharge, thus supporting agricultural and domestic water needs [38]. Similarly, community engagement and strengthening of\u00a0RWHS are considered as strategic policies to handle risks related to excessive rainfall and floods in\u00a0India [66]. Meanwhile, Tunisia established a\u00a0hydro-social strategy based on investments in\u00a0soil and water infrastructure to improve the\u00a0collection and reuse of\u00a0stormwater [67]. Also, Bangladesh confronts extreme meteorological conditions and uncontrolled water usage, which make is necessary to implement community-based RWHS (CBRWHS) and promote government financial and technical support to boost RWH installations in\u00a0coastal locations [68]. Moreover, including RWHS in\u00a0water management strategies and empowering local governance to design and maintain\u00a0these hydraulic structures in\u00a0LMICs will reduce the\u00a0negative impact of\u00a0flooding, drought, and unpredictable water availability in\u00a0these regions [8]. Additionally, adopting natural-based solutions to rehabilitate degraded water infrastructure and engaging local communities in\u00a0water management policies in\u00a0Africa\u2019s\u00a0arid and semi-arid lands will reduce land degradation and enhance water supply for agriculture and domestic usage [3]. Despite differences in\u00a0governance, climate conditions, and technologies across regions, the\u00a0literature recommends that integrating RWHS into broader climate adaptation and water security strategies can\u00a0effectively support sustainable development in\u00a0water-scarce areas. However, the\u00a0success of\u00a0such initiatives largely depends on the\u00a0active participation of\u00a0all actors, including policymakers, researchers, investors, and local communities, in\u00a0the\u00a0planning, implementation, and management of\u00a0these hydraulic structures.<\/p>\n<h2>CONCLUSION<\/h2>\n<p>The\u00a0current paper presents a\u00a0systematic review of\u00a0RWHS studies using the\u00a0PRISMA approach. The\u00a0review includes publications from January 2021 to December 2025, sourced from ScienceDirect and Scopus databases, with a\u00a0focus on articles indexed in\u00a0Scopus.<\/p>\n<p>A\u00a0comprehensive analysis of\u00a066 selected articles has been conducted to develop an\u00a0in-depth literature review that highlights various aspects of\u00a0RWHS, emphasizing their vital role in\u00a0water resource management, particularly in\u00a0arid and semi-arid areas experiencing severe droughts and water scarcity.<\/p>\n<p>The\u00a0study synthesizes ancestral RWH practices and explores their cultural significance across the\u00a0Middle East, Asia, North Africa, and Sub-Saharan\u00a0Africa. It also gives insights into their modernization efforts, especially the\u00a0integration of\u00a0new technologies and advancements in\u00a0developing sustainable solutions for water shortage and flood control.<\/p>\n<p>This review underscores the\u00a0importance of\u00a0innovative methods employed worldwide to identify potential sites of\u00a0RWH structures, considering the\u00a0diversity of\u00a0types, designs, and socio-economic and environmental parameters. Such an\u00a0approach assists decision-makers and investors in\u00a0identifying suitable locations for implementing various types of\u00a0RWHS.<\/p>\n<p>Despite the\u00a0dual benefits of\u00a0RWHS in\u00a0providing water to enhance agriculture, cattle, and rural livelihoods, as well as mitigating floods and water erosion, these systems are yet to be fully integrated into water management policies of\u00a0several water-scarce countries. Challenges for sustainable water resource management using RWHS include raising consciousness and education among rural communities regarding the\u00a0use and conservation of\u00a0these hydraulic structures, as well as establishing strong institutional support mechanisms.<\/p>\n<p>In\u00a0conclusion, future research should focus on evaluating governmental and institutional frameworks to expand the\u00a0adoption of\u00a0RWHS in\u00a0arid and semi-arid regions, promoting their role as a\u00a0sustainable technique to mitigate water deficiency.<\/p>\n<p><em>\u00a0<\/em><\/p>\n","protected":false},"excerpt":{"rendered":"<p>In a climate marked by prolonged drought, observed mainly in arid and semi-arid areas, the installation of hydraulic systems for rainwater collection and storage in rural and isolated areas is becoming a necessity to preserve livestock and ensure water security for the local popula-tion. For this purpose, this review synthesizes recent studies on the various hydraulic systems used for rainwater harvesting (RWH) in rural areas to support agriculture, livestock, and households. This review examines 66 relevant studies published in journals indexed in ScienceDirect and Scopus over a period of five years (January 2021 \u2013 December 2025). It emphasizes the importance of design based on the specific characteristics of each location or country, the criteria for selecting implementation sites, the impact of RWH systems on agricul-ture, livestock, and rural households, existing challenges, and proposes some guidelines for sustainable rainwater management and flood reduction.<\/p>\n","protected":false},"author":8,"featured_media":39142,"comment_status":"closed","ping_status":"closed","sticky":false,"template":"","format":"standard","meta":{"_acf_changed":false,"footnotes":""},"categories":[94,86],"tags":[4138,3517,121,542,4165,3854,4141,4164,2559],"coauthors":[4106,4107],"class_list":["post-39147","post","type-post","status-publish","format-standard","has-post-thumbnail","hentry","category-current-issue","category-hydraulics-hydrology-and-hydrogeology","tag-arid","tag-climate","tag-drought","tag-flood","tag-hydraulic-systems","tag-rainwater","tag-rainwater-harvesting-rwh","tag-semi-arid-areas","tag-water-erosion"],"acf":[],"_links":{"self":[{"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/posts\/39147","targetHints":{"allow":["GET"]}}],"collection":[{"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/posts"}],"about":[{"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/types\/post"}],"author":[{"embeddable":true,"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/users\/8"}],"replies":[{"embeddable":true,"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/comments?post=39147"}],"version-history":[{"count":5,"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/posts\/39147\/revisions"}],"predecessor-version":[{"id":39204,"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/posts\/39147\/revisions\/39204"}],"wp:featuredmedia":[{"embeddable":true,"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/media\/39142"}],"wp:attachment":[{"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/media?parent=39147"}],"wp:term":[{"taxonomy":"category","embeddable":true,"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/categories?post=39147"},{"taxonomy":"post_tag","embeddable":true,"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/tags?post=39147"},{"taxonomy":"author","embeddable":true,"href":"https:\/\/www.vtei.cz\/en\/wp-json\/wp\/v2\/coauthors?post=39147"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}