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Search Results (563)

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5 pages, 642 KiB  
Proceeding Paper
Optimal Location of Best Management Practices for Flood Mitigation in Urban Drainage Systems
by Enrico Creaco, Arianna Dada, Giovanna Grossi and Sara Todeschini
Eng. Proc. 2024, 69(1), 189; https://doi.org/10.3390/engproc2024069189 - 14 Oct 2024
Viewed by 43
Abstract
The present work presents a bi-objective optimization methodology, which is aimed at simultaneously minimizing the total installation costs of management systems as well as urban flooding, as a tool to be conveniently adopted as part of a decision support system to help identify [...] Read more.
The present work presents a bi-objective optimization methodology, which is aimed at simultaneously minimizing the total installation costs of management systems as well as urban flooding, as a tool to be conveniently adopted as part of a decision support system to help identify the optimal location of best management practices (BMPs). For each sub-catchment present in an urban drainage system, the decision variables include the rate of impervious areas to be used for BMP installation. The performance of the urban drainage system following optimal BMP installation is tested against climate change scenarios obtained from a real case study conducted in the industrial area of Brescia; the numerical model of this study can be obtained via the EPASWMM software. Full article
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<p>Case study network (<b>a</b>) and Chicago hyetograph (<b>b</b>) used in EPASWMM.</p>
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<p>Pareto front of optimal solutions in the trade-off between costs and flooding volume.</p>
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30 pages, 3379 KiB  
Review
Review of Green Water Systems for Urban Flood Resilience: Literature and Codes
by Sebastián Valencia-Félix, Johan Anco-Valdivia, Alain Jorge Espinoza Vigil, Alejandro Víctor Hidalgo Valdivia and Carlos Sanchez-Carigga
Water 2024, 16(20), 2908; https://doi.org/10.3390/w16202908 - 13 Oct 2024
Viewed by 470
Abstract
Achieving Urban Flood Resilience (UFR) is essential for modern societies, requiring the implementation of effective practices in different countries to mitigate hydrological events. Green Water Systems (GWSs) emerge as a promising alternative to achieve UFR, but they are still poorly explored and present [...] Read more.
Achieving Urban Flood Resilience (UFR) is essential for modern societies, requiring the implementation of effective practices in different countries to mitigate hydrological events. Green Water Systems (GWSs) emerge as a promising alternative to achieve UFR, but they are still poorly explored and present varied definitions. This article aims to define GWSs within the framework of sustainable practices and propose a regulation that promotes UFR. Through a systematic review of existing definitions and an analysis of international regulations on sustainable urban drainage systems (SuDSs), this study uncovers the varied perceptions and applications of GWSs and their role in Blue–Green Infrastructure (BGI). Furthermore, the research puts forth a standardized definition of GWSs and emphasizes the implementation of SuDSs in Peru. This approach aims to address the existing knowledge gap and contribute to the advancement of sustainable urban infrastructure. Full article
(This article belongs to the Special Issue Stormwater Management in Sponge Cities)
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<p>Number of people affected by floods around the world from 2000 to 2024.</p>
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<p>Number of deaths from floods around the world from 2000 to 2024.</p>
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<p>Population affected in Peru from 2015 to 2023 by floods.</p>
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<p>Number of deaths in Peru from 2015 to 2023 due to floods.</p>
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<p>Flow chart of optimized flood management in relation to existing sustainable tools based on gray, green, and blue infrastructure. Adapted from [<a href="#B13-water-16-02908" class="html-bibr">13</a>].</p>
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<p>Methodology diagram.</p>
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<p>Flowchart for literature review based on [<a href="#B31-water-16-02908" class="html-bibr">31</a>].</p>
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<p>Number of documents per country assigned to this search.</p>
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<p>Distribution of papers in the different research areas of the second search model.</p>
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<p>Variables considered for proposing a definition of GWSs.</p>
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<p>The continuity line frames GWS as a current sustainable tool that combines fundamental pillars of green infrastructure, nature-based solutions, and sustainable urban drainage systems, integrated with water capture and infiltration systems (BI) to manage and handle urban flooding.</p>
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23 pages, 8642 KiB  
Article
The Impact of Green Infrastructure on the Quality of Stormwater and Environmental Risk
by Izabela Godyń, Agnieszka Grela, Krzysztof Muszyński and Justyna Pamuła
Sustainability 2024, 16(19), 8530; https://doi.org/10.3390/su16198530 - 30 Sep 2024
Viewed by 717
Abstract
Increasing urbanization and the associated sealing of areas and the use of storm sewer systems for drainage not only increase the risk of flooding but also reduce water quality in streams into which stormwater is discharged. Green infrastructure (GI) measures are applied with [...] Read more.
Increasing urbanization and the associated sealing of areas and the use of storm sewer systems for drainage not only increase the risk of flooding but also reduce water quality in streams into which stormwater is discharged. Green infrastructure (GI) measures are applied with the aim of managing this stormwater sustainably and reducing the associated risks. To this end, a quantitative–qualitative approach was developed to simulate GI—namely, rain gardens, bioretention cells, and vegetative bioswales—at the urban catchment scale. The findings highlight the potential of applying GI measures to managing stormwater more effectively in urban environments and mitigating its negative pollution-related impacts. For the housing estate analyzed, a simulated implementation of GI resulted in a reduction in pollution, measured as total nitrogen (N; 9–52%), nitrate-N (5–30%), total phosphorus (11–59%), chemical oxygen demand (8–46%), total suspended solids (13–73%), copper (12–64%), zinc (Zn; 16–87%), polycyclic aromatic hydrocarbons (16–91%), and the hydrocarbon oil index (HOI; 15–85%). Reducing the concentrations of pollutants minimizes the risk to human health determined via the HOI from a low-risk level to zero risk and reduces the ecological risk in terms of Zn pollution from a significant risk to a low risk of adverse effects. The modeling conducted clearly shows that the GI solutions implemented facilitated a quantitative reduction and a qualitative improvement in stormwater, which is crucial from an environmental perspective and ensures a sustainable approach to stormwater management. Lowering the levels of stormwater pollution through the implementation of GI will consequently lower the environmental burden of pollutants in urban areas. Full article
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<p>Location of the area analyzed with the division of the catchment area into four existing outlets.</p>
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<p>(<b>a</b>) Digital Terrain Model (DTM), runoff flow paths, and storm sewage system. (<b>b</b>) Imperviousness of the study area and subcatchment delineation (SWMM interface).</p>
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<p>Flowchart of research methodology.</p>
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<p>Location of GI facilities.</p>
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<p>Simulation results in reduction in stormwater for RGs, BRCs, and VSs.</p>
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<p>Reduction in concentrations at outlets (W1–W4) and in the entire area (All).</p>
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<p>Average reduction in the HQ and RQ in the entire area.</p>
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25 pages, 7731 KiB  
Article
A Low-Impact Development-Based Modeling Framework for Flood Mitigation in a Coastal Community
by Enis Baltaci and Latif Kalin
Water 2024, 16(19), 2772; https://doi.org/10.3390/w16192772 - 29 Sep 2024
Viewed by 558
Abstract
Urbanization is known to increase the volume of stormwater runoff and peak flow rates, which leads to changes in the natural flow regime and increases the likelihood of flooding. Low-impact development (LID) practices seek to reduce runoff volume and peak flow and are [...] Read more.
Urbanization is known to increase the volume of stormwater runoff and peak flow rates, which leads to changes in the natural flow regime and increases the likelihood of flooding. Low-impact development (LID) practices seek to reduce runoff volume and peak flow and are generally considered to be a more sustainable solution for urban stormwater management. In this study, we present a systematic approach to address nuisance flooding issues in small cities and communities. As an application, the effectiveness of two LID practices, rain barrels and permeable pavements, were explored in mitigating the urban flooding problem of a highly urbanized small coastal watershed in Alabama, USA. The EPA Stormwater Management Model (SWMM) was first calibrated for water depth using data collected at multiple sites within the watershed during the 2014–2015 period. The calibrated model was then used to first identify the areas prone to flooding using design storms with 1, 2, 5-, 10-, 50-, and 100-year return periods. Floodplain maps were generated for those design storms with HEC-RAS. Next, LID options upstream of those flood-prone areas were assessed to potentially minimize the flooding risks. The results indicate that LID controls can have considerable benefits for stormwater management by reducing runoff volume (1–24%), peak flow rates (18–25%), and water depth (5–15%), potentially returning watersheds to their natural flow regimes, thereby minimizing the flooding risk in urbanized areas. However, the effectiveness of LIDs, especially for the runoff volume, quickly diminishes as the return periods of the storms increase. Rain barrels were identified as the most economical and effective LID within the drainage system. Full article
(This article belongs to the Special Issue Urbanization, Climate Change and Flood Risk Management)
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<p>Location and Boundary of the Toulmins Spring Branch Watershed.</p>
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<p>Hydrometeorological conditions for the study period.</p>
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<p>Hydrologic and hydraulic model of Toulmins spring branch watershed by SWMM.</p>
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<p>Observed and simulated water depth exceedance curves at the sites.</p>
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<p>Observed and simulated maximum depths during large storms using rainfall data from both rain gauge and radar at the sites.</p>
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<p>A 100 yr return period floodplain map of TSBW shown on aerial photo.</p>
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<p>Flood-generating area index at junction 20.</p>
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<p>Reduction in peak flow, depth, and runoff volume at junction 20 based on subwatershed 34 under the use of various LIDs and with different return periods.</p>
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<p>Reduction in peak flow, depth, and runoff volume at junction 20 based on subwatershed 35 under the use of various LIDs and with different return periods.</p>
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<p>Variation in peak flows at junction 20 (<b>A</b>) and 28 (<b>B</b>) under various return periods with and without LID (only rain barrels were considered) implemented at subwatershed 35 and 36, respectively.</p>
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<p>Reduction in peak flow, depth, and runoff volume at junction 28 based on subwatershed 36 under the use of various LIDs and with different return periods.</p>
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<p>Comparison of radar and rain gauge data for the 16 May 2015–18 May 2015 period (<b>top</b>) and comparison of observed water depths to simulated ones with radar and rain gauge data forcing (<b>bottom</b>).</p>
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<p>The channel clogged by vegetation and trash at site 5.</p>
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<p>Rain barrels were installed at Prichard house.</p>
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16 pages, 1937 KiB  
Article
Community Governance Performance of Nature-Based Solutions for Sustainable Urban Stormwater Management in Sub-Saharan Africa
by Simon Peter Muwafu, Louis Celliers, Jürgen Scheffran and María Máñez Costa
Sustainability 2024, 16(19), 8328; https://doi.org/10.3390/su16198328 - 25 Sep 2024
Viewed by 690
Abstract
The expansion of cities in Sub-Saharan Africa has led to an increase in impervious surfaces, intensifying stormwater management challenges, especially in informal settlements situated in ecologically sensitive areas like wetlands. This urban growth has heightened flood risks and negatively impacted biodiversity, water quality, [...] Read more.
The expansion of cities in Sub-Saharan Africa has led to an increase in impervious surfaces, intensifying stormwater management challenges, especially in informal settlements situated in ecologically sensitive areas like wetlands. This urban growth has heightened flood risks and negatively impacted biodiversity, water quality, and socio-economic conditions, particularly during extreme weather events intensified by climate change. Nature-Based Solutions (NbSs), including Sustainable Urban Drainage Systems (SUDSs), offer sustainable strategies for managing stormwater and mitigating these adverse effects. However, the success of such solutions relies not only on their technical implementation but also on the social and institutional contexts within urban communities. Community-level governance is crucial in integrating NbSs into urban stormwater management frameworks. This research evaluates how community governance of NbSs, specifically SUDSs, can enhance stormwater management and flood resilience in Kampala, Uganda. Using an assessment framework grounded in the Policy Arrangement Approach (PAA)—which considers discourses, actors, resources, and rules of engagement—this study incorporates structural, social, and political factors that influence SUDS community governance performance. Concentrating on the Sembule zones within the Nalukolongo catchment area, this research investigates the impact of community governance dynamics on SUDS implementation. This study examines key aspects such as community engagement, resource management, and regulatory frameworks to assess the effectiveness of these initiatives, providing valuable insights for advancing nature-based urban stormwater management. Full article
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<p>Aging drainage systems, commonly obstructed by refuse.</p>
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<p>Structure of evaluation process.</p>
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<p>Performance of determinants under the resources dimension.</p>
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<p>Performance of determinants under the rules of engagement dimension.</p>
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<p>Performance of determinants under the actors dimension.</p>
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<p>Performance of determinants under the discourses dimension.</p>
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<p>Combined performance within and across dimensions.</p>
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19 pages, 3396 KiB  
Article
Urban Flood Vulnerability Assessment in Freetown, Sierra Leone: AHP Approach
by Abdulai Osman Koroma, Mohamed Saber and Cherifa Abdelbaki
Hydrology 2024, 11(10), 158; https://doi.org/10.3390/hydrology11100158 - 25 Sep 2024
Viewed by 804
Abstract
This study presents a comprehensive flood vulnerability assessment for Freetown, Sierra Leone, spanning the period from 2001 to 2022. The objective of this research was to assess the temporal and spatial changes in the flood vulnerability using Geographic Information System (GIS) tools and [...] Read more.
This study presents a comprehensive flood vulnerability assessment for Freetown, Sierra Leone, spanning the period from 2001 to 2022. The objective of this research was to assess the temporal and spatial changes in the flood vulnerability using Geographic Information System (GIS) tools and AHP-based Multi-Criteria Decision-Making (MCDM) analysis. This study identified the flood-vulnerable zones (FVZs) by integrating critical factors such as the rainfall, NDVI, elevation, slope, drainage density, TWI, distance to road, distance to river, and LULC. The analysis reveals that approximately 60% of the study area is classified as having medium to high vulnerability, with a significant 20% increase in the flood risk observed over the past two decades. In 2001, very-high-vulnerability zones covered about 68.84 km2 (10% of the total area), with high-vulnerability areas encompassing 137.68 km2 (20%). By 2020, very-high-vulnerability zones remained constant at 68.84 km2 (10%), while high-vulnerability areas decreased to 103.26 km2 (15%), and medium-vulnerability zones expanded from 206.51 km2 (30%) in 2001 to 240.93 km2 (35%). The AHP model-derived weights reflect the varied significance of the flood-inducing factors, with rainfall (0.27) being the most critical and elevation (0.04) being the least. A consistency ratio (CR) of 0.068 (< 0.1) confirms the reliability of these weights. The spatial–temporal analysis highlights the east and southeast regions of Freetown as consistently vulnerable over the years, while infrastructure improvements in other areas have contributed to a general decrease in very-high-vulnerability zones. This research highlights the urgent need for resilient urban planning and targeted interventions to mitigate future flood impacts, offering clear insights into the natural and human-induced drivers of the flood risk for effective hazard mitigation and sustainable urban development. Full article
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<p>(<b>a</b>) Map of Freetown; (<b>b</b>) map of Africa; (<b>c</b>) map of Africa.</p>
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<p>Flowchart showing dataset integration of the study area.</p>
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<p>(<b>a</b>) Map of annual rainfall for Freetown 2001; (<b>b</b>) map of annual rainfall for Freetown 2010; (<b>c</b>) annual rainfall for Freetown 2020 (source: Esri ArcGIS 10.8).</p>
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<p>Slope map of Freetown (source: Esri ArcGIS).</p>
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<p>(<b>a</b>) LULC map of Freetown 2001; (<b>b</b>) LULC map of Freetown 2010; (<b>c</b>) LULC map of Freetown 2020 (source: Esri ArcGIS).</p>
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<p>(<b>a</b>) Drainage density map of Freetown; (<b>b</b>) distance-from-road map of Freetown (source: Esri ArcGIS).</p>
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<p>(<b>a</b>) TWI map of Freetown; (<b>b</b>) distance-from-river map of Freetown (source: Esri ArcGIS).</p>
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<p>(<b>a</b>) NDVI map of Freetown; (<b>b</b>) elevation map of Freetown (source: Esri ArcGIS).</p>
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<p>(<b>a</b>) Flood vulnerability map 2001; (<b>b</b>) flood vulnerability map 2010; (<b>c</b>) flood vulnerability map 2020 (source: Esri ArcGIS).</p>
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17 pages, 2199 KiB  
Review
Stormwater Management in Urban Coastal Areas—A Review
by António Geraldes, Francisco Piqueiro, Cristina Santos and Cristina Matos
Water 2024, 16(19), 2717; https://doi.org/10.3390/w16192717 - 24 Sep 2024
Viewed by 604
Abstract
Stormwater management in coastal urban cities, where drainage networks are influenced by marine dynamics and specific soil and altimetry conditions, has specific challenges that need to be addressed to ensure adequate management in such areas, which are also heavily affected by floods. Their [...] Read more.
Stormwater management in coastal urban cities, where drainage networks are influenced by marine dynamics and specific soil and altimetry conditions, has specific challenges that need to be addressed to ensure adequate management in such areas, which are also heavily affected by floods. Their location downstream of drainage basins and the interaction of network outfalls with current and tidal variability increases the vulnerability of populations and should therefore be the target of specific studies. This article presents a literature review, where publications that focus on stormwater management in coastal urban areas were identified and analyzed. The main objective was to present the key issues related to drainage in coastal areas, the most relevant challenges, the solutions and strategies that reveal the greater potential for application and the challenges for modeling this type of case. It is intended to provide a grounded basis for new ways of optimizing stormwater drainage in coastal areas and promote a sustainable urban water cycle. This review reveals the necessity to implement a multidisciplinary approach to minimize three main issues: urban flooding, stormwater pollution and groundwater salinization, including the adaptation of existing infrastructures, complementing them with control solutions at source, correct urban planning and the involvement of populations. For an effective management of urban stormwater drainage in coastal areas, this approach must be carried out on a watershed scale, duly supported by reliable decision support tools and monitoring systems. Full article
(This article belongs to the Special Issue Urban Drainage Systems and Stormwater Management)
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<p>Methodological flowchart.</p>
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<p>Year of publication of the articles that make up the portfolio.</p>
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<p>Spatial distribution of the studies covered in the portfolio (the values in the circles are the number of publications in each location).</p>
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<p>The interconnection of the GI, NbS and LID concepts.</p>
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30 pages, 17772 KiB  
Article
The Effects of Flood Damage on Urban Road Networks in Italy: The Critical Function of Underpasses
by Laura Turconi, Barbara Bono, Rebecca Genta and Fabio Luino
Land 2024, 13(9), 1493; https://doi.org/10.3390/land13091493 - 14 Sep 2024
Viewed by 1402
Abstract
The urban areas of Mediterranean Europe, and particularly Italy, have experienced considerable expansion since the late 19th century in terms of settlements, structures, and infrastructure, especially in large population centers. In such areas, the geohydrological risk is high not only for inhabited areas [...] Read more.
The urban areas of Mediterranean Europe, and particularly Italy, have experienced considerable expansion since the late 19th century in terms of settlements, structures, and infrastructure, especially in large population centers. In such areas, the geohydrological risk is high not only for inhabited areas but also along roadways exposed to flooding. This scenario is worrying, especially in road underpass sections, where drivers are unlikely to perceive a real risk due to the high degree of confidence that comes from the habit of driving. Underpasses have been widely used to obviate the need to find shorter alternative routes and manage vehicular traffic in urban settings impeded by previous anthropogenic and natural constraints. To assess the numerical consistency, frequency, and areal distribution of flood risk around road underpasses, several hundred pieces of data were selected (mostly from international, national and local newspapers, CNR IRPI archive and local archives) and cataloged in a thematic database, referring mainly to the Italian territory. The behavioral aspects in the face of risk were also examined in order to provide a better understanding and raise awareness for preventive purposes. The results of this specific CNR research, which lasted about two years, confirm the exposure of underpasses to extreme risk events, affecting road users. In Italy alone, between 1942 and 2023, 698 underpasses were identified as having experienced a flooding event at least once. The database shows that 680 vehicles were involved in Italy, with a total of at least 812 individuals, of whom 19 died. Despite incomplete and uneven information, the findings of the analysis regarding the increment in underpasses flooding and the drivers action in front of a flooded underpass may be useful for undertaking the appropriate mitigation strategies. Full article
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<p>Flooded underpasses analyzed in the dataset [<a href="#B40-land-13-01493" class="html-bibr">40</a>,<a href="#B41-land-13-01493" class="html-bibr">41</a>,<a href="#B42-land-13-01493" class="html-bibr">42</a>,<a href="#B43-land-13-01493" class="html-bibr">43</a>,<a href="#B44-land-13-01493" class="html-bibr">44</a>,<a href="#B45-land-13-01493" class="html-bibr">45</a>] that occurred in Italian areas in the past and in recent years. (<b>a</b>) Historical image of flooded underpass that occurred in Turin city (Piedmont, northwestern Italy) published in a national newspaper in 1983; (<b>b</b>) Sant’Elena, near Padua city, in Oriental Alps River Basin Districts in 2014; (<b>c</b>) Tradate city, in Po River Basin Districts in 2017; (<b>d</b>) Palermo city, in Sicily River Basin Districts in 2018; (<b>e</b>) Castellanza city, near Varese, in Po River Basin Districts in 2023; (<b>f</b>) Riccione city, in Central Appennine River Basin Districts in 2023.</p>
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<p>Subdivision of Italy by RBDs according to Floods Directive 2007/60/EC [<a href="#B48-land-13-01493" class="html-bibr">48</a>,<a href="#B49-land-13-01493" class="html-bibr">49</a>].</p>
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<p>Diachronic mapping of built-up area in a representative urban region, Grosseto city, Tuscany, North Appennine RBD (data source: CNR-IRPI archive). From left to right, the use of historical maps (1843) and remote sensing data in the form of aerial photographs, from 1954 (as reported in the central image of the figure) to early 2000s, and satellite imagery from the early 2000s to today is presented.</p>
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<p>Comparison of urbanized areas per CLC, 1990 and 2018 [<a href="#B51-land-13-01493" class="html-bibr">51</a>], per RBD. For each RBD, there is an increment on urbanized square kilometers, especially Po, Oriental Alps, and South Appennine RBD.</p>
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<p>Number of floods in whole Italian territory caused by heavy rain. Since 2018, there is a significant increment of this type of events and the increment is still ongoing [<a href="#B77-land-13-01493" class="html-bibr">77</a>].</p>
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<p>Example of integrated analysis of data planimetric variations of a short stretch of Stura di Lanzo River, northwest of Torino (Piemonte Region, Po RBD), period 1878–2000, obtained from the transposition of pattern in a GIS project of historical maps and aerial photographs found at CNR-IRPI in Turin and satellite images.</p>
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<p>Width reductions in terminal stretches of Roja River in coastal plains (Ventimiglia, Liguria, North Appennine RBD) measured via GIS using historical maps (1836) and current satellite images (2023).</p>
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<p>Distribution of underpasses obtained from technical maps [<a href="#B91-land-13-01493" class="html-bibr">91</a>] overlapping flooded areas in 2016 flood in Piedmont (Po RBD). Black dots indicate the underpasses manually individuated, while red dots indicate the underpasses present in Piedmont Cadastre. This flood could have a significant increment of flooded underpasses reported. The red outline indicates the urbanized area (as per 2018 CLC).</p>
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<p>Distribution of flooded underpasses in RBD areas, 1942–2023 (identified by the color of the outline shown in <a href="#land-13-01493-f002" class="html-fig">Figure 2</a>).</p>
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<p>Trends in Italian population (black line) and number of vehicles registered in Italy (green line) since 1942, in relation to surveyed flooded underpasses (red line). A steady increase in vehicles and higher number of floods since 2010 can be seen. The availability of online news and easier retrieval of data allowed details for the last 15 years. This graph does not consider the effect of changes in rainfall.</p>
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<p>Annual distribution of flooding events at surveyed underpasses in Italy by RBD, 2014–2023.</p>
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<p>Seasonal distribution of flooding events of surveyed underpasses in Italy by RBD.</p>
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<p>Starting from aerial and satellite images (<b>a</b>,<b>d</b>), proceeding with the restitution in flooded areas maps (<b>b</b>,<b>e</b>), finally it is possible to identify the underpasses affected by the flooding events (<b>c</b>,<b>f</b>). The example in the figure illustrates the 1994 (<b>a</b>–<b>c</b>) and the 2016 (<b>d</b>–<b>f</b>) flood event in Alessandria municipality (Piemonte region, Po RBD) (areas in blue), captured by aerial photography or satellite images (CNR IRPI archives and [<a href="#B92-land-13-01493" class="html-bibr">92</a>]). The dots in light blue indicate the underpasses flooded, while the red ones indicate the remaining ones recorded in the Piemonte Cadastre. In this area, the database obtained from the search of newspaper sources alone did not identify any underpasses involved neither in the 1994 event nor in the 2016 one. The areas affected by floods are in the same location most of the time (<b>g</b>), causing a reiteration in flooded underpasses (<b>h</b>). All flooded underpasses are located in a PGRA class [<a href="#B48-land-13-01493" class="html-bibr">48</a>,<a href="#B49-land-13-01493" class="html-bibr">49</a>].</p>
Full article ">Figure 13 Cont.
<p>Starting from aerial and satellite images (<b>a</b>,<b>d</b>), proceeding with the restitution in flooded areas maps (<b>b</b>,<b>e</b>), finally it is possible to identify the underpasses affected by the flooding events (<b>c</b>,<b>f</b>). The example in the figure illustrates the 1994 (<b>a</b>–<b>c</b>) and the 2016 (<b>d</b>–<b>f</b>) flood event in Alessandria municipality (Piemonte region, Po RBD) (areas in blue), captured by aerial photography or satellite images (CNR IRPI archives and [<a href="#B92-land-13-01493" class="html-bibr">92</a>]). The dots in light blue indicate the underpasses flooded, while the red ones indicate the remaining ones recorded in the Piemonte Cadastre. In this area, the database obtained from the search of newspaper sources alone did not identify any underpasses involved neither in the 1994 event nor in the 2016 one. The areas affected by floods are in the same location most of the time (<b>g</b>), causing a reiteration in flooded underpasses (<b>h</b>). All flooded underpasses are located in a PGRA class [<a href="#B48-land-13-01493" class="html-bibr">48</a>,<a href="#B49-land-13-01493" class="html-bibr">49</a>].</p>
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<p>Percentage distribution of the underpasses flooding causes for the complete database (period 1942–2023) (<b>a</b>) and for the reduced period 2010–2023 (<b>b</b>) in the four categories considered (pluvial flooding, urban flooding, fluvial flooding, coastal flooding).</p>
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<p>Underpass flooding in each RBD, 2010–2023, in relation to cumulative annual rainfall.</p>
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<p>Distribution of underpass flooding events by flood warning system and PGRA class (%). Red indicates underpasses without preventive measures, and green indicates underpasses with prevention.</p>
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<p>Distribution of vehicle involvement during flooding events of surveyed underpasses by time slot: 00:01 to 06:00 a.m., 06:01 to 12:00 p.m., 12:01 to 06:00 p.m., and 06:01 to 12:00 a.m. (night, morning, afternoon, and evening, respectively). The sample includes only the 195 events for which information was available.</p>
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<p>Behavior of some drivers in front of flooded underpass during event of 10 March 2024 in Monza province (Northern Italy, Po RBD). Different reactions can be observed: Vehicles in red circles pass, encouraged by van’s passing, which is higher off the ground than cars. The vehicle in the yellow circle stops, but it is unclear whether it will proceed further. A similar indication may have been apparent for the observer filming from the opposite side of the scene. There is nothing to suggest whether he too passed through flooded subway or merely filmed the scene. There is no reason to assume that the observer called for help or dissuaded drivers from going toward the underpass from his direction. The vehicle in the green circle was the only one to leave the underpass, reversing its direction, probably seeking an alternative route. No guards had been put in place by responsible parties or volunteers. There is no indication as to whether this underpass has signs warning of potential flooding (modified video frame from [<a href="#B99-land-13-01493" class="html-bibr">99</a>]).</p>
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<p>Flooded underpass during the event of May 2024 near Milan (Po RBD).</p>
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14 pages, 1319 KiB  
Article
Future Scenarios of Design Rainfall Due to Upcoming Climate Changes in NSW, Australia
by Iqbal Hossain, Shirley Gato-Trinidad, Monzur Imteaz and Scott Rayburg
Atmosphere 2024, 15(9), 1101; https://doi.org/10.3390/atmos15091101 - 10 Sep 2024
Viewed by 358
Abstract
The occurrence of rainfall is significantly affected by climate change around the world. While in some places this is likely to result in increases in rainfall, both winter and summer rainfall in most parts of New South Wales (NSW), Australia are projected to [...] Read more.
The occurrence of rainfall is significantly affected by climate change around the world. While in some places this is likely to result in increases in rainfall, both winter and summer rainfall in most parts of New South Wales (NSW), Australia are projected to decrease considerably due to climate change. This has the potential to impact on a range of hydraulic and hydrologic design considerations for water engineers, such as the design and construction of stormwater management systems. These systems are currently planned based on past extreme rain event data, and changes in extreme rainfall amounts due to climate change could lead to systems being seriously undersized (if extreme precipitation events become more common and/or higher in magnitude) or oversized (if extreme rainfall events become less frequent or decrease in magnitude). Both outcomes would have potentially serious consequences. Consequently, safe, efficient, and cost-effective urban drainage system design requires the consideration of impacts arising from climate change on the approximation of design rainfall. This study examines the impacts of climate change on the probability of occurrence of daily extreme rainfall in New South Wales (NSW), Australia. The analysis was performed for 29 selected meteorological stations located across NSW. Future design rainfall in this research was determined from the projected rainfall for different time periods (2020 to 2039, 2040 to 2059, 2060 to 2079, and 2080 to 2099). The results of this study show that design rainfall for the standard return periods was, in most cases, lower than that derived employing the design rainfall obtained from the Australian Bureau of Meteorology (BoM). While most of the analysed meteorological stations showed significantly different outcomes using the climate change scenario data, this varied considerably between stations and different time periods. This suggests that more work needs to be performed at the local scale to incorporate climate change predicted rainfall data into future stormwater system designs to ensure the best outcomes. Full article
(This article belongs to the Special Issue Statistical Approaches in Climatic Parameters Prediction)
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<p>Annual average rainfall for NSW over the 1991–2020 period.</p>
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<p>The relative position of the rainfall stations in NSW, Australia that were used to generate future scenarios of design rainfall due to upcoming climate change.</p>
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<p>Framework for identifying the influence of climate change effects on design rainfall [<a href="#B22-atmosphere-15-01101" class="html-bibr">22</a>]. The processes inside the red dotted box are performed by the Australian Bureau of Meteorology. The blue arrows show how the process progresses from one step to the next.</p>
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<p>Visual representation of return level estimation for different recurrence intervals for all the periods of extreme rainfall. Symbols ‘a’ represents 1900–2019, ‘b’ represents 2020–2039, ‘c’ represents 2040–2059, ‘d’ represents 2060–2079, and ‘e’ represents 2080–2099. The lines on the left of the figure represent the dendrogram which shows the structure of the cluster for rainfall stations.</p>
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<p>Design rainfall comparison between ARR and projected rainfall for different time periods for four selected meteorological stations. The symbols (<b>A</b>–<b>D</b>) are for different meteorological stations as shown.</p>
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4 pages, 675 KiB  
Proceeding Paper
Impact of Infiltration Systems on Illicit Waters in Sewer Networks
by Anita Raimondi, Tecla Casari and Umberto Sanfilippo
Eng. Proc. 2024, 69(1), 108; https://doi.org/10.3390/engproc2024069108 - 10 Sep 2024
Viewed by 159
Abstract
The frequent effects of urbanization and climate change make stormwater runoff control critical. Infiltration systems can provide multiple benefits to the environment, i.e., flood risk mitigation, stormwater quality improvement, aquifer recharge, and a reduction in the activation of combined sewer overflows. However, their [...] Read more.
The frequent effects of urbanization and climate change make stormwater runoff control critical. Infiltration systems can provide multiple benefits to the environment, i.e., flood risk mitigation, stormwater quality improvement, aquifer recharge, and a reduction in the activation of combined sewer overflows. However, their use must be carefully planned since they can cause illicit waters in the sewer network due to the deterioration of pipes and junctions. This study proposes a theoretical framework and a case study to assess the interaction between the deterioration of a sewer and the infiltration coming from the soil surface and/or from infiltration systems. Full article
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<p>Schematization of the control volume. <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>Q</mi> </mrow> <mrow> <mi>i</mi> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math>: inflow rate in the sewer pipeline; <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>Q</mi> </mrow> <mrow> <mi>p</mi> <mo>,</mo> <mi>i</mi> </mrow> </msub> </mrow> </semantics></math>: illicit flow rate; <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>Q</mi> </mrow> <mrow> <mi>o</mi> <mi>u</mi> <mi>t</mi> </mrow> </msub> </mrow> </semantics></math>: outflow rate from the sewer pipeline; <math display="inline"><semantics> <mrow> <mi>P</mi> </mrow> </semantics></math>: rainfall; <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>h</mi> </mrow> <mrow> <mi>c</mi> <mi>i</mi> </mrow> </msub> </mrow> </semantics></math>: water depth in the pipe; <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>h</mi> </mrow> <mrow> <mi>c</mi> </mrow> </msub> </mrow> </semantics></math>: height of the pipe from the bottom; <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>h</mi> </mrow> <mrow> <mi>f</mi> </mrow> </msub> </mrow> </semantics></math>: groundwater level; <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>Q</mi> </mrow> <mrow> <mi>a</mi> </mrow> </msub> </mrow> </semantics></math>: infiltration rate.</p>
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<p>Illicit flow in the considered sewer for different values of rainfall intensity and transmittance coefficient.</p>
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28 pages, 13830 KiB  
Article
Integrated Geospatial and Geostatistical Multi-Criteria Evaluation of Urban Groundwater Quality Using Water Quality Indices
by Iram Naz, Hong Fan, Rana Waqar Aslam, Aqil Tariq, Abdul Quddoos, Asif Sajjad, Walid Soufan, Khalid F. Almutairi and Farhan Ali
Water 2024, 16(17), 2549; https://doi.org/10.3390/w16172549 - 9 Sep 2024
Cited by 2 | Viewed by 841
Abstract
Groundwater contamination poses a severe public health risk in Lahore, Pakistan’s second-largest city, where over-exploited aquifers are the primary municipal and domestic water supply source. This study presents the first comprehensive district-wide assessment of groundwater quality across Lahore using an innovative integrated approach [...] Read more.
Groundwater contamination poses a severe public health risk in Lahore, Pakistan’s second-largest city, where over-exploited aquifers are the primary municipal and domestic water supply source. This study presents the first comprehensive district-wide assessment of groundwater quality across Lahore using an innovative integrated approach combining geographic information systems (GIS), multi-criteria decision analysis (MCDA), and water quality indexing techniques. The core objectives were to map the spatial distributions of critical pollutants like arsenic, model their impacts on overall potability, and evaluate targeted remediation scenarios. The analytic hierarchy process (AHP) methodology was applied to derive weights for the relative importance of diverse water quality parameters based on expert judgments. Arsenic received the highest priority weight (0.28), followed by total dissolved solids (0.22) and hardness (0.15), reflecting their significance as health hazards. Weighted overlay analysis in GIS delineated localized quality hotspots, unveiling severely degraded areas with very poor index values (>150) in urban industrial zones like Lahore Cantt, Model Town, and parts of Lahore City. This corroborates reports of unregulated industrial effluent discharges contributing to aquifer pollution. Prospective improvement scenarios projected that reducing heavy metals like arsenic by 30% could enhance quality indices by up to 20.71% in critically degraded localities like Shalimar. Simulating advanced multi-barrier water treatment processes showcased an over 95% potential reduction in arsenic levels, indicating the requirement for deploying advanced oxidation and filtration infrastructure aligned with local contaminant profiles. The integrated decision support tool enables the visualization of complex contamination patterns, evaluation of remediation options, and prioritizing risk-mitigation investments based on the spatial distribution of hazard exposures. This framework equips urban planners and utilities with critical insights for developing targeted groundwater quality restoration policies through strategic interventions encompassing treatment facilities, drainage infrastructure improvements, and pollutant discharge regulations. Its replicability across other regions allows for tackling widespread groundwater contamination challenges through robust data synthesis and quantitative scenario modeling capabilities. Full article
(This article belongs to the Special Issue Groundwater Quality and Human Health Risk, 2nd Edition)
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<p>Map of the study area: Lahore District.</p>
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<p>Flow chart of methodology.</p>
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<p>Parameters results: (<b>a</b>) pH, (<b>b</b>) turbidity, (<b>c</b>) TDS, (<b>d</b>) EC, and (<b>e</b>) hardness.</p>
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<p>Parameter results: (<b>a</b>) calcium, (<b>b</b>) magnesium, (<b>c</b>) alkalinity, (<b>d</b>) chloride, and (<b>e</b>) arsenic.</p>
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<p>Groundwater quality AHP index.</p>
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<p>Scenario I (variation in heavy metals): (<b>a</b>) 10%, (<b>b</b>) 20%, and (<b>c</b>) 30% reduction.</p>
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<p>Scenario II (variation in chemical parameters): (<b>a</b>) Chemical 10%, (<b>b</b>) Chemical 20%, (<b>c</b>) Chemical 30%.</p>
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<p>Variation in primary treatment. (<b>a</b>) Part A with a 40% reduction in the total dissolved solids (TDSs) and (<b>b</b>) Part B with a 60% reduction in the total dissolved solids (TDSs).</p>
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<p>Variation in secondary treatment. (<b>a</b>) Part A with a 65% reduction in the total dissolved solids (TDSs) and 45% reduction in hardness and (<b>b</b>) Part B with an 80% reduction in the total dissolved solids (TDSs) and 55% reduction in hardness.</p>
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<p>Variation in tertiary treatment. (<b>a</b>) Part A with 90% reduction in arsenic and (<b>b</b>) Part B with 95% reduction in arsenic.</p>
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19 pages, 4096 KiB  
Article
The Causes of Waterlogging in Chinese Southern Hilly Cities Based on Hydrological Processes
by Bei Li, Sheng Jiao, Yuan Zhou and Min Zhou
Sustainability 2024, 16(17), 7804; https://doi.org/10.3390/su16177804 - 7 Sep 2024
Viewed by 455
Abstract
The various hydrological processes that cause waterlogging exhibit regional differences. Studies on the causes of waterlogging in Chinese southern hilly cities from the perspective of urban regional hydrological processes are needed. This article examines Changsha Central City to study the hydrological processes of [...] Read more.
The various hydrological processes that cause waterlogging exhibit regional differences. Studies on the causes of waterlogging in Chinese southern hilly cities from the perspective of urban regional hydrological processes are needed. This article examines Changsha Central City to study the hydrological processes of Chinese southern hilly cities based on waterlogging point data from 2015 to 2017, analyzing the relationships between the degree of waterlogging and changes in the material elements of runoff sources, runoff convergence terminals, and runoff convergence processes using correlation analysis, principal component analysis and comparative analysis. These results show that the urban waterlogging in Chinese southern hilly cities is caused by the hardening of convergence spaces, concentrated water distribution, a decrease in the connectivity of rainwater corridors, complex topographic slopes, and a lag in the construction of drainage facilities. The expansion of impervious surfaces, particularly in areas intended for convergence terminals, has significantly reduced the number of these critical structures. Additionally, disordered changes in topographic slopes, the division caused by roads, and the hardening of underlying surfaces in rainwater corridors have collectively diminished the structural and ecological connectivity of the rainwater corridor system. This obstruction of surface runoff into concentrated water bodies has rendered the runoff regulation function of these water bodies ineffective, making their size a leading cause of urban waterlogging. To mitigate the risk of waterlogging, Chinese southern hilly cities should prevent urban development from encroaching on natural runoff areas. They should also implement dispersed water body layouts, enhance both the structural and ecological connectivity of rainwater corridors and their underlying surfaces, and improve the design standards of drainage facilities. Full article
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<p>Location and watershed units map of Changsha Central City.</p>
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<p>Spatial distribution of waterlogging points in the study area: (<b>a</b>) the degree of waterlogging in watershed units; (<b>b</b>) distribution of waterlogging points, rainwater corridors, and conflict points between rainwater corridors and roads.</p>
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<p>(<b>a</b>) Distribution of land cover with different elevations, (<b>b</b>) distribution of land cover with different slopes.</p>
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<p>The land use and cover maps for Changsha Central City in 1990 and 2017: (<b>a</b>) 1990; (<b>b</b>) 2017.</p>
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<p>Changes in water body distribution and slope in Changsha Central City from 1990 to 2017: (<b>a</b>) water body distribution; (<b>b</b>) slope.</p>
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4 pages, 1113 KiB  
Proceeding Paper
Improving the Performance of Bayesian Decision Networks for Water Quality Sensor Deployment in UDNs through a Reduced Search Domain
by Mariacrocetta Sambito and Antonietta Simone
Eng. Proc. 2024, 69(1), 58; https://doi.org/10.3390/engproc2024069058 - 4 Sep 2024
Viewed by 186
Abstract
The contamination of urban drainage systems (UDNs) represents a serious threat to the environment and public health. Treatment plants are often inefficient in their removal, making timely identification and isolation interventions necessary. In this regard, various monitoring strategies have been proposed, among which [...] Read more.
The contamination of urban drainage systems (UDNs) represents a serious threat to the environment and public health. Treatment plants are often inefficient in their removal, making timely identification and isolation interventions necessary. In this regard, various monitoring strategies have been proposed, among which the Bayesian decision network (BDN) approach has proven to be very effective, although also very complex. To reduce their level of complexity, it is usual to optimize them using approaches based on preconditioning. The present work fits into this framework by proposing a two-phase strategy aimed at identifying an optimal monitoring system for UDNs. The first phase involves reducing the search domain of the system using a complex network theory (CNT) topological metric adapted to infrastructure systems; the second phase implements the Bayesian approach to the new search space to optimize the position of the sensors in the network. The results are promising and reveal that the strategy could be valuable to water utilities. Full article
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<p>Results for the classic Bayesian (<b>left</b>) approach and the proposed two-phase strategy (<b>right</b>).</p>
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12 pages, 8555 KiB  
Article
An Experimental Study of the Retention Effect of Urban Drainage Systems in Response to Grate Inlet Clogging
by Seongil Yeom and Jungkyu Ahn
Sustainability 2024, 16(17), 7596; https://doi.org/10.3390/su16177596 - 2 Sep 2024
Viewed by 627
Abstract
The rainfall drainage characteristics of urban areas result in more surface runoff compared to soil surfaces. Conventional Urban Drainage Systems, CUDs, have disadvantages when managing this surface runoff, leading to urban water circulation issues such as flooding and depletion of groundwater. The performance [...] Read more.
The rainfall drainage characteristics of urban areas result in more surface runoff compared to soil surfaces. Conventional Urban Drainage Systems, CUDs, have disadvantages when managing this surface runoff, leading to urban water circulation issues such as flooding and depletion of groundwater. The performance of CUDs varies significantly depending on the clogging of grate inlets with various debris and shapes. To address these disadvantages, Sustainable Urban Drainage Systems, SUDs, have been proposed. This study compares the drainage efficiency of the two systems; using a physical model with an artificial rainfall simulator, an experimental study was conducted with respect to clogging type, clogging ratio, and rainfall intensity. Comparative analysis of peak flow rates and the peak time demonstrates the advantages of IRDs. As a result, IRDs are applicable to the mitigation of urban water circulation problems such as inundation. Full article
(This article belongs to the Section Sustainable Water Management)
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<p>Example of clogging on a grate inlet. (<b>a</b>) Complete clogging on road; (<b>b</b>) partial clogging on O-shaped channel.</p>
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<p>Schematic diagram of IRDs [<a href="#B19-sustainability-16-07596" class="html-bibr">19</a>].</p>
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<p>Diagram of physical model: (<b>a</b>) components; (<b>b</b>) specification of surface area.</p>
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<p>Detail of grate inlet: (<b>a</b>) OCs; (<b>b</b>) IRDs.</p>
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<p>Detail of surface area: (<b>a</b>) specification of pavement; (<b>b</b>) result of sieve test.</p>
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<p>Diagram and example of clogging types: (<b>a</b>) Expansion-type clogging; (<b>b</b>) Contraction-type clogging; (<b>c</b>) example of Contraction-type clogging; (<b>d</b>) example of Expansion-type clogging.</p>
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<p>Flowchart of experimental study.</p>
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<p>Measurement of runoff. (<b>a</b>) OCs; (<b>b</b>) IRDs.</p>
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<p>Measurement of surface water depth. (<b>a</b>) IN30; (<b>b</b>) IN60; (<b>c</b>) IN90.</p>
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<p>Accumulative discharge of physical model: (<b>a</b>) IRDs-E; (<b>b</b>) IRDs-C; (<b>c</b>) OCs-E; (<b>d</b>) OCs-C.</p>
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<p>Comparison of peak time, <span class="html-italic">T<sub>p</sub></span>.</p>
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<p>Dimensionless comparison of <span class="html-italic">T</span>*.</p>
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13 pages, 12658 KiB  
Article
Research and Prevention of Harmful Gases in Special Structures of Urban Deep Drainage Systems
by Hao Liu
Water 2024, 16(17), 2481; https://doi.org/10.3390/w16172481 - 31 Aug 2024
Viewed by 464
Abstract
Wastewater remaining in pipes for extended periods can create anaerobic environments, fostering the growth of anaerobic bacteria and producing harmful gases such as methane and hydrogen sulfide. Additionally, certain structures within drainage systems, such as drop shafts and vertical shafts, induce turbulent flow, [...] Read more.
Wastewater remaining in pipes for extended periods can create anaerobic environments, fostering the growth of anaerobic bacteria and producing harmful gases such as methane and hydrogen sulfide. Additionally, certain structures within drainage systems, such as drop shafts and vertical shafts, induce turbulent flow, causing the release of dissolved harmful gases, which pose significant risks to public health and urban infrastructure. This study focused on the investigation and analysis of vertical shafts with helical tray structures in drainage systems. Using ANSYS 2021 R2 software, simulations of the shafts were conducted by employing the standard k-ε turbulence model and Eulerian multiphase flow method to simulate the shaft’s operation and obtain various parameters of hydrogen sulfide release. Concurrently, a scale model constructed in the laboratory was used to study and analyze the release of hydrogen sulfide gas dissolved in water from this type of structure. Combining the simulation and laboratory experiments, the hydrogen sulfide gas release rate from water in this structure was 0.05–0.4%. This research provides a reference for the study and control of hydrogen sulfide gas release. Full article
(This article belongs to the Special Issue Advances in Biological Technologies for Wastewater Treatment)
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<p>Simulation experimental model.</p>
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<p>Model meshing.</p>
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<p>Experimental shaft model.</p>
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<p>Morphological transformation of sulfides under different pH environments.</p>
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<p>Experimental system diagram.</p>
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<p>Experimental water tank.</p>
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<p>Gas detector.</p>
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<p>Experimental circulation system.</p>
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<p>Hydrogen sulfide gas volume fraction contour map in the vertical shaft at different times.</p>
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<p>Monitoring points in the simulation model.</p>
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<p>Hydrogen sulfide volume fraction curves at three different inflow speeds: (<b>a</b>) V = 0.05 m/s; (<b>b</b>) V = 0.075 m/s; (<b>c</b>) V = 0.1 m/s.</p>
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<p>Hydrogen sulfide concentration curves at three different inflow speeds: (<b>a</b>) V = 0.05 m/s; (<b>b</b>) V = 0.075 m/s; (<b>c</b>) V = 0.1 m/s.</p>
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<p>Hydrogen sulfide concentration curves at three different sulfide ion concentrations: (<b>a</b>) C, S<sup>2−</sup> = 10 mg/L; (<b>b</b>) C, S<sup>2−</sup> = 20 mg/L; (<b>c</b>) C, S<sup>2−</sup> = 40 mg/L.</p>
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