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Water, Volume 16, Issue 24 (December-2 2024) – 79 articles

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21 pages, 1617 KiB  
Article
Challenges of Providing Safe Drinking Water in African Rural Communities: A Case Study on the Oio Region, Guinea-Bissau
by Pedro Silveira, Maria Teresa Rebelo and Daniel Salvador
Water 2024, 16(24), 3621; https://doi.org/10.3390/w16243621 (registering DOI) - 16 Dec 2024
Abstract
Access to safe drinking water is a fundamental human right, yet it remains a global challenge affecting nearly 2 billion people, particularly in Africa in regions such as Guinea-Bissau. This study investigated the microbiological and physicochemical quality of drinking water in four rural [...] Read more.
Access to safe drinking water is a fundamental human right, yet it remains a global challenge affecting nearly 2 billion people, particularly in Africa in regions such as Guinea-Bissau. This study investigated the microbiological and physicochemical quality of drinking water in four rural areas of the Oio region of Guinea-Bissau—Cangha N’Tchugal, Cajaque, Infaidi and Insanha—over a one-year period (October 2022–September 2023) to assess water safety and seasonal variations. During this period, eight water samples were collected and analysed from each site, split evenly between the dry and wet seasons. The results showed widespread faecal coliform contamination, with concentrations escalating during the wet season (2 to 39 CFU/100 mL), posing a health risk. Physicochemical analysis showed consistently acidic pH values (from 4.93 to 6.58) and seasonal variations in phosphate and iron concentrations, with a marked decrease in iron concentrations during the wet season. These results indicated that the water from the four sampling points was unfit for human consumption. In light of these findings, there is an urgent need for the regular monitoring of water sources used for drinking and for improved access to resources and basic sanitation in the future. Full article
(This article belongs to the Section Water Quality and Contamination)
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<p>Location of the study areas in Encheia, Bissorã sector. Author’s map.</p>
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<p>Representation of the study area and the sampling points in the localities of Cangha N’Tchugal, Cajaque, Infaidi, and Insanha. Map and photographs by the authors.</p>
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<p>Study flowchart.</p>
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<p>Concentration of faecal coliforms (CFU/100 mL) in water samples from the study localities: Cangha N’Tchugal (n = 8) 0 to 9.0 CFU/100 mL; Cajaque (n = 8) 26.0 to 50.0 CFU/100 mL; Infaidi (n = 8) 1.0 to 50 CFU/100 mL; and Insanha (n = 8) 1.0 to 30.0 CFU/100 mL.</p>
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22 pages, 1902 KiB  
Review
Production, Toxicological Effects, and Control Technologies of Ochratoxin A Contamination: Addressing the Existing Challenges
by Yan Yang, Mingtao Li, Junxiong Zhao, Jingxuan Li, Kangwen Lao and Fuqiang Fan
Water 2024, 16(24), 3620; https://doi.org/10.3390/w16243620 (registering DOI) - 16 Dec 2024
Abstract
Ochratoxin A (OTA) is a mycotoxin commonly found in food and feed. It presents a serious threat to human and animal health while also posing a risk as a potential aquatic contaminant. Although many research efforts have been placed on OTA contamination and [...] Read more.
Ochratoxin A (OTA) is a mycotoxin commonly found in food and feed. It presents a serious threat to human and animal health while also posing a risk as a potential aquatic contaminant. Although many research efforts have been placed on OTA contamination and detoxification, systematic and in-depth studies on summarizing its primary sources, formation mechanisms, toxicological effects, and control technologies remain essential. This review systematically analyzed the sources of OTA contamination, including the main toxin-producing strains and their specific colonization environments, in which the biosynthetic pathways and key regulatory factors of OTA were outlined. On this basis, the principle, merits, disadvantages, and application potential of OTA control technologies, including the physical, chemical, and biological detoxification techniques, were comparatively evaluated. The applications of genetic engineering with an emphasis on newly identified degradative enzymes and their potential in OTA removal were carefully elucidated. Considering the stringent global OTA regulatory standards and food safety handling requirements, this review highlights the necessity of comprehensive control measure development and emphasizes the importance of rigorous technical evaluation and regulatory approval. The aim is to provide theoretical support for effective OTA control and to guide future OTA contamination management in complex environments. Full article
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<p>The molecular structure of naturally occurring OTs.</p>
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<p>Hypothetical OTA Biosynthetic Pathway [<a href="#B50-water-16-03620" class="html-bibr">50</a>].</p>
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<p>Proposed OTA biosynthetic gene cluster.</p>
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<p>OTA biosynthetic gene clusters in different fungi (redraw after [<a href="#B50-water-16-03620" class="html-bibr">50</a>]).</p>
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<p>The biodegradation mechanisms of OTA.</p>
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14 pages, 5637 KiB  
Article
Rapid Start-Up of Anammox Process with a Stepwise Strategy: System Performance, Microbial Community Succession and Mechanism Exploration
by Sha Wang, Yangxin Yin, Yueyao Gao, Fang Li and Jian Zhou
Water 2024, 16(24), 3619; https://doi.org/10.3390/w16243619 (registering DOI) - 16 Dec 2024
Viewed by 85
Abstract
Anammox has emerged as a primary alternative to conventional biological nitrogen removal because of its excellent nitrogen removal performance and minimal energy utilization. However, the slow growth and reproduction of anammox bacteria (AnAOB) leads to an overlong start-up period, which severely restricts the [...] Read more.
Anammox has emerged as a primary alternative to conventional biological nitrogen removal because of its excellent nitrogen removal performance and minimal energy utilization. However, the slow growth and reproduction of anammox bacteria (AnAOB) leads to an overlong start-up period, which severely restricts the full-scale promotion and application of anammox in wastewater treatment plants. Therefore, in this study, a sequencing batch biofilm reactor (SBBR) equipped with combined packing was used to investigate the rapid start-up of the anammox process. The result showed that the anammox reactor started successfully in only 75 days using a stepwise strategy, and the total nitrogen removal rate (TNRR) increased from 0.02 kg N m−3 d−1 on day 1 to 0.23 kg N m−3 d−1 on day 75. The primary AnAOB was Candidatus Kuenenia with a relative abundance of 37.20% at the end of the start-up of the anammox reactor. Denitrifying bacteria, nitrifying bacteria, and hydrolytic bacteria were also detected in the reactor. The synergistic interactions between AnAOB and these bacteria facilitated the efficient removal of pollutants. This study can offer a potential approach for the start-up of anammox in domestic wastewater treatment plants, which is conducive to achieving widespread application of anammox. Full article
(This article belongs to the Special Issue ANAMMOX Based Technology for Nitrogen Removal from Wastewater)
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<p>Experimental schematic diagram of the SBBR.</p>
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<p>Nitrogen removal performance of the anammox reactor during start-up; (<b>a</b>) NH<sub>4</sub><sup>+</sup>-N; (<b>b</b>) NO<sub>2</sub><sup>−</sup>-N; (<b>c</b>) NO<sub>3</sub><sup>−</sup>-N; (<b>d</b>) TN; inf: influent, eff: effluent.</p>
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<p>The R<sub>p</sub> and R<sub>s</sub> in anammox reactor.</p>
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<p>Variations in nitrogen in typical cycles: (<b>a</b>) day 21; (<b>b</b>) day 30; (<b>c</b>) day 75.</p>
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<p>Microbial community structure of inoculated sludge and anammox system: (<b>a</b>) phylum level; (<b>b</b>) genus level.</p>
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<p>Schematic diagram of nitrogen metabolism in anammox system.</p>
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18 pages, 1899 KiB  
Review
Methane Production Mechanism and Control Strategies for Sewers: A Critical Review
by Feng Hou, Shuai Liu, Wan-Xin Yin, Li-Li Gan, Hong-Tao Pang, Jia-Qiang Lv, Ying Liu, Ai-Jie Wang and Hong-Cheng Wang
Water 2024, 16(24), 3618; https://doi.org/10.3390/w16243618 (registering DOI) - 16 Dec 2024
Viewed by 192
Abstract
Methane (CH4) emissions from urban sewer systems represent a significant contributor to greenhouse gases, driven by anaerobic decomposition processes. This review elucidates the mechanisms underlying CH4 production in sewers, which are influenced by environmental factors such as the COD/SO4 [...] Read more.
Methane (CH4) emissions from urban sewer systems represent a significant contributor to greenhouse gases, driven by anaerobic decomposition processes. This review elucidates the mechanisms underlying CH4 production in sewers, which are influenced by environmental factors such as the COD/SO42− ratio, temperature, dissolved oxygen, pH, flow rate, and hydraulic retention time. We critically evaluated the effectiveness of empirical, mechanistic, and machine learning (ML) models in predicting CH4 emissions, highlighting the limitations of each. This review further examines control strategies, including oxygen injection, iron salt dosing, and nitrate application, emphasizing the importance of balancing CH4 reduction with the operational efficiency of wastewater treatment plants (WWTPs). An integrated approach combining mechanistic and data-driven models is advocated to enhance prediction accuracy and optimize CH4 management across urban sewer systems. Full article
(This article belongs to the Section Urban Water Management)
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<p>Biochemical reactions in sewer systems.</p>
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<p>Study on factors affecting methane production in sewers. (<b>a</b>) Statistical correlations between both sewer CH<sub>4</sub> and CO<sub>2</sub> emissions and overlying sewage COD in a field survey [<a href="#B24-water-16-03618" class="html-bibr">24</a>]. (<b>b</b>) Comparison of CH<sub>4</sub> emissions at the end of sewage pipe networks between summer and winter [<a href="#B27-water-16-03618" class="html-bibr">27</a>]. (<b>c</b>) Changes in dissolved oxygen in biofilms with biofilm thickness, COD = 400 mg/L [<a href="#B28-water-16-03618" class="html-bibr">28</a>]. (<b>d</b>) H<sub>2</sub>S production, CH<sub>4</sub> production, and cell viability, where sewer biofilms were subjected to pH levels of 10.5, 11.5, and 12.5, respectively, for 6 hb [<a href="#B29-water-16-03618" class="html-bibr">29</a>]. (<b>e</b>) Variation in biomass density at different wall shear stresses; COD = 400 mg/L (F means wall shear stress, Pa) [<a href="#B28-water-16-03618" class="html-bibr">28</a>].</p>
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<p>Sewage network-related model. (<b>a</b>) Model defects. (<b>b</b>) Gas generation mechanism [<a href="#B9-water-16-03618" class="html-bibr">9</a>,<a href="#B53-water-16-03618" class="html-bibr">53</a>]. (<b>c</b>) Organic matter transformation in a sewage network [<a href="#B54-water-16-03618" class="html-bibr">54</a>]. (<b>d</b>) Machine learning model with different principles [<a href="#B7-water-16-03618" class="html-bibr">7</a>].</p>
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<p>Transformation of ferric salt in an urban water system [<a href="#B67-water-16-03618" class="html-bibr">67</a>].</p>
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12 pages, 4355 KiB  
Article
Effect of Seepage on Sand Levee Failure Due to Lateral Overtopping
by Woochul Kang, Seongyun Kim and Eunkyung Jang
Water 2024, 16(24), 3617; https://doi.org/10.3390/w16243617 (registering DOI) - 16 Dec 2024
Viewed by 119
Abstract
Recent increases in rainfall duration and intensity due to climate change have heightened the importance of levee stability. However, previous studies on levee failure, primarily caused by seepage and overtopping, have mostly examined these causes independently owing to their distinct characteristics. In this [...] Read more.
Recent increases in rainfall duration and intensity due to climate change have heightened the importance of levee stability. However, previous studies on levee failure, primarily caused by seepage and overtopping, have mostly examined these causes independently owing to their distinct characteristics. In this study, we conducted lateral overtopping failure experiments under seepage conditions that closely resembled those in experiments conducted in previous studies. Seepage was monitored using water pressure sensors and a distributed optical fiber cable that provided continuous heat for temperature monitoring in the levee. Τhe analysis of levee failure due to lateral overtopping, in the presence of seepage, was conducted using image analysis with digitization techniques and machine learning-based color segmentation techniques on the protected lowland side of the levee, targeting the same area. The results revealed that levee failure occurred more than twice as fast in experiments where seepage conditions were considered compared to the experiments where they were not. Thus, levees weakened by seepage are more vulnerable to overtopping and breaching. Consequently, employing a comprehensive approach that integrates various monitoring and analysis methods for assessing levee stability is preferable to relying on a single method alone. Full article
(This article belongs to the Special Issue Safety Monitoring of Hydraulic Structures)
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<p>The process of building a full-scale sand levee for the experiment and the final result.</p>
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<p>(<b>a</b>) Point cloud results generated from experimenting on the overtopping and breaching of a sand levee in 2021 [<a href="#B3-water-16-03617" class="html-bibr">3</a>] using imagery prior to overtopping, and (<b>b</b>) comparison of point clouds generated from experimenting on the seepage of a sand levee in 2023 [<a href="#B4-water-16-03617" class="html-bibr">4</a>] using imagery prior to overtopping and breaching.</p>
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<p>Grain size distribution results of particles comprising the sand levee of the experiment conducted in 2021 [<a href="#B3-water-16-03617" class="html-bibr">3</a>] and grain size distribution results of particles comprising a levee in the sand levee seepage and overtopping and breaching experiment conducted in 2023 [<a href="#B4-water-16-03617" class="html-bibr">4</a>].</p>
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<p>Specifications of the levee and locations of the installed sensors.</p>
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<p>Measurement result of flow supplied to reproduce seepage in the levee.</p>
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<p>Measurement results of water pressure changed by seepage in the levee.</p>
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<p>(<b>a</b>) Photo of the levee seepage experiment and (<b>b</b>) leakage and flooding of the protected lowland as a result of seepage.</p>
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<p>Temperature changes due to seepage at 0.5 m below the bottom of the protected lowland.</p>
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<p>Temperature variations due to seepage at different heights in the same location.</p>
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<p>(<b>a</b>) Image analysis results of the levee failure process and (<b>b</b>) comparison of the levee surface loss.</p>
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<p>Color-based levee failure image analysis using K-means clustering (<b>a</b>) 2 classification, (<b>b</b>) 3 classification, and (<b>c</b>) 5 classification.</p>
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26 pages, 2256 KiB  
Review
Recent Progress on Surface Water Quality Models Utilizing Machine Learning Techniques
by Mengjie He, Qin Qian, Xinyu Liu, Jing Zhang and James Curry
Water 2024, 16(24), 3616; https://doi.org/10.3390/w16243616 (registering DOI) - 15 Dec 2024
Viewed by 644
Abstract
Surface waterbodies are heavily exposed to pollutants caused by natural disasters and human activities. Empowering sensor technologies in water quality monitoring, sufficient measurements have become available to develop machine learning (ML) models. Numerous ML models have quickly been adopted to predict water quality [...] Read more.
Surface waterbodies are heavily exposed to pollutants caused by natural disasters and human activities. Empowering sensor technologies in water quality monitoring, sufficient measurements have become available to develop machine learning (ML) models. Numerous ML models have quickly been adopted to predict water quality indicators in various surface waterbodies. This paper reviews 78 recent articles from 2022 to October 2024, categorizing water quality models utilizing ML into three groups: Point-to-Point (P2P), which estimates the current target value based on other measurements at the same time point; Sequence-to-Point (S2P), which utilizes previous time series data to predict the target value at one time point ahead; and Sequence-to-Sequence (S2S), which uses previous time series data to forecast sequential target values in the future. The ML models used in each group are classified and compared according to water quality indicators, data availability, and model performance. Widely used strategies for improving performance, including feature engineering, hyperparameter tuning, and transfer learning, are recognized and described to enhance model effectiveness. The interpretability limitations of ML applications are discussed. This review provides a perspective on emerging ML for surface water quality models. Full article
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<p>Summary of the main traditional models and deep learning models in this review.</p>
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<p>Proportions of different ML models applied on P2P, S2P, and S2S models.</p>
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<p>The architecture of the CNN-LSTM model.</p>
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<p>The bi-directional architecture of the BiLSTM model.</p>
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<p>The architecture of the AT-BiLSTM model with ED structure.</p>
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<p>Proportion of metrics used in ML water quality regression models.</p>
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18 pages, 6768 KiB  
Article
An Interpretable CatBoost Model Guided by Spectral Morphological Features for the Inversion of Coastal Water Quality Parameters
by Baofeng Chen, Yunzhi Chen and Hongmei Chen
Water 2024, 16(24), 3615; https://doi.org/10.3390/w16243615 (registering DOI) - 15 Dec 2024
Viewed by 359
Abstract
Chlorophyll-a (Chla) and total suspended solid (TSS) concentrations are important parameters for water quality assessment, and in recent years, machine learning has been shown to have great potential in this field. However, current water quality parameter inversion models lack interpretability and rarely consider [...] Read more.
Chlorophyll-a (Chla) and total suspended solid (TSS) concentrations are important parameters for water quality assessment, and in recent years, machine learning has been shown to have great potential in this field. However, current water quality parameter inversion models lack interpretability and rarely consider the morphological characteristics of the spectrum. To address this limitation, we used Sentinel-3 OLCI data to construct an interpretable CatBoost model guided by spectral morphological characteristics for remote sensing monitoring of Chla and TSS along the coast of Fujian. The results show that the coastal waters of Fujian Province can be divided into five clusters, and the areas of different clusters will change with the alternation of seasons. Clusters 2 and 4 are the main types of coastal waters. The CatBoost model combined with spectral feature engineering has a high accuracy in predicting Chla and TSS, among which Chla is slightly better than TSS (R2 = 0.88, MSE = 8.21, MAPE = 1.10 for Chla predictions; R2 = 0.77, MSE = 380.49, MAPE = 2.48 for TSS predictions). We further conducted an interpretability analysis on the model output and found that the combination of BRI and TBI indexes composed of bands such as b8, b9, and b10 and the fluctuation of spectral curves will have a significant impact on the prediction of model output. The interpretable CatBoost model based on spectral morphological features proposed in this study can provide an effective technical means of estimating the chlorophyll-a and total suspended particulate matter concentrations in the coastal areas of Fujian. Full article
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<p>Location of Fujian Province and study area.</p>
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<p>GLORIA data points used in the study.</p>
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<p>Research flow chart.</p>
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<p>(<b>a</b>) Average spectral curve of each category. (<b>b</b>) Chla concentration distribution of different clusters. (<b>c</b>) TSS concentration distribution of different clusters.</p>
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<p>Clustering results of coastal water bodies in Fujian Province in different seasons. Figures (<b>a</b>–<b>d</b>) show the average maps of water classification for spring, summer, autumn, and winter.</p>
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<p>The structure of the CatBoost algorithm.</p>
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<p>Prediction results of the CatBoost model on the test set (the red line is the trend line).</p>
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<p>Interpretability results of spectral features for CatBoost inversion model of Chla and TSS by SHAP analysis. Figure (<b>a</b>) shows the local explainable results of Chla, Figure (<b>b</b>) shows the global explainable results of Chla, Figure (<b>c</b>) shows the local explainable results of TSS, and Figure (<b>d</b>) shows the global explainable results of TSS. (In the left column chart, one dot represents a sample, where warmer colors indicate larger values of the feature, and vice versa. The wider the distribution of SHAP values for a feature, the larger its global SHAP value, indicating that the feature has a greater impact on the model. In the right column chart, the white numbers on the blue bar represent the average absolute SHAP value [<a href="#B44-water-16-03615" class="html-bibr">44</a>].)</p>
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<p>Annual average concentration distribution map of Chla and TSS along the coast of Fujian Province from 2021 to 2023. (<b>a</b>–<b>c</b>) is the average concentration of Chla, and (<b>d</b>–<b>f</b>) is the average concentration of TSS.</p>
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<p>Average Chla and TSS concentration values in different seasons along the coast of Fujian Province from 2021 to 2023. The four graphs on the left (<b>a</b>–<b>d</b>) show the average concentration of Chla, while the four graphs on the right (<b>e</b>–<b>h</b>) show the average concentration of TSS.</p>
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12 pages, 21792 KiB  
Article
Distribution and Affecting Factors of Aragonite Saturation in the Northern South China Sea in Summer
by Ping Han, Zhaojun Wang, Honggang Lv, Feiyong Chen, Xuewan Zhang and Jin Wang
Water 2024, 16(24), 3614; https://doi.org/10.3390/w16243614 (registering DOI) - 15 Dec 2024
Viewed by 370
Abstract
Based on the carbonate and hydrological parameters of a survey made in August–September 2011, we investigated the distribution and affecting factors of aragonite saturation (Ωarag) in the northern South China Sea. The levels of Ωarag were found to gradually decrease [...] Read more.
Based on the carbonate and hydrological parameters of a survey made in August–September 2011, we investigated the distribution and affecting factors of aragonite saturation (Ωarag) in the northern South China Sea. The levels of Ωarag were found to gradually decrease with depth in the northern South China Sea. Surface-water Ωarag values ranged from 2.56 to 3.68, with the highest value occurring in the region of Pearl River-diluted water near the northern coast. The increase in Ωarag due to primary production, stimulated by the Pearl River freshwater input, exceeded the decrease in Ωarag due to the direct input of low-Ωarag fresh water, resulting in high Ωarag in that area. In contrast, Ωarag levels below 2 generally appeared in subsurface water below 50 m in depth. Intense community respiration was the main reason for the low Ωarag. By 2100, bottom-water Ωarag levels could be lower than 1.7, and even the undersaturation of aragonite could appear, due to the oceanic absorption of atmospheric CO2. Full article
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<p>The geographical location of the study area. Sampling stations are marked by rhombuses.</p>
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<p>Distributions of salinity (<b>a</b>,<b>b</b>), temperature (<b>c</b>,<b>d</b>), and DO% (<b>e</b>,<b>f</b>) in the surface and bottom waters of the northern South China Sea.</p>
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<p>Distributions of salinity (<b>a</b>,<b>b</b>), temperature (<b>c</b>,<b>d</b>), and DO% (<b>e</b>,<b>f</b>) in the surface and bottom waters of the northern South China Sea.</p>
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<p>Depth profiles of salinity (<b>a</b>–<b>d</b>), temperature (°C) (<b>e</b>–<b>h</b>), and DO% (<b>i</b>–<b>l</b>) in Transects A–D (the horizontal axis represents the offshore distance (m), the vertical axis represents the water depth (m), and gray represents the land). Sampling stations are marked by dots.</p>
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<p>Distributions of DIC (μmol kg<sup>−1</sup>, (<b>a</b>,<b>b</b>), TAlk (μmol kg<sup>−1</sup>, (<b>c</b>,<b>d</b>), and Ω<sub>arag</sub> (<b>e</b>,<b>f</b>) in the surface and bottom waters of the northern South China Sea. Sampling stations are marked by dots.</p>
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<p>Depth profiles of DIC (μmol kg<sup>−1</sup>, (<b>a</b>–<b>d</b>), TAlk (μmol kg<sup>−1</sup>, (<b>e</b>–<b>h</b>), and Ω<sub>arag</sub> (<b>i</b>–<b>l</b>) in Transects A–D (the horizontal axis represents the offshore distance (m), the vertical axis represents the water depth (m), and gray represents the land). Sampling stations are marked by dots.</p>
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<p>Relationship between AOU and ΔDIC in the subsurface northern South China Sea (the dashed line indicates the Redfield ratio).</p>
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<p>(<b>a</b>) The relationship between AOU and Ω<sub>arag</sub>; (<b>b</b>) the relationship between ΔDIC and Ω<sub>arag</sub> in the subsurface of the northern South China Sea.</p>
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<p>Predicted surface (<b>a</b>) and bottom (<b>b</b>) Ω<sub>arag</sub> values in the northern South China Sea in 2100.</p>
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<p>Profile of predicted Ω<sub>arag</sub> values in the northern South China Sea in 2100 in Transect A–D (Corresponding subfigures (<b>a</b>–<b>d</b>)).</p>
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20 pages, 3072 KiB  
Review
Spatiotemporal Dynamics of Suspended Particulate Matter in Water Environments: A Review
by Trung Tin Huynh, Jaein Kim, Sang Deuk Lee, Michael Fettweis, Qilong Bi, Sangsik Kim, Sungyun Lee, Yun Young Choi, Huu Son Nguyen, Trong Vinh Bui and Byung Joon Lee
Water 2024, 16(24), 3613; https://doi.org/10.3390/w16243613 (registering DOI) - 15 Dec 2024
Viewed by 396
Abstract
Suspended particulate matter (SPM) is an indispensable component of water environments. Its fate and transport involve various physical and biogeochemical cycles. This paper provides a comprehensive review of SPM dynamics by integrating insights from biogeochemical processes, spatiotemporal observation techniques, and numerical modeling approaches. [...] Read more.
Suspended particulate matter (SPM) is an indispensable component of water environments. Its fate and transport involve various physical and biogeochemical cycles. This paper provides a comprehensive review of SPM dynamics by integrating insights from biogeochemical processes, spatiotemporal observation techniques, and numerical modeling approaches. It also explores methods for diagnosing SPM-mediated biogeochemical processes, such as the flocculation kinetics test and organic matter composition analysis. Advances in remote sensing, in situ monitoring, and high-resolution retrieval algorithms are discussed, highlighting their significance in detecting and quantifying SPM concentrations across varying spatial and temporal scales. Furthermore, this review examines integrated models that incorporate population balance equations on the basis of flocculation kinetics into multi-dimensional sediment transport models. The results from this study provide valuable insights into SPM dynamics, ultimately enhancing our knowledge of SPM behavior and transport in water environments. However, uncertainties remain due to limited field data on flocculation kinetics and the need for parameter optimization in numerical models. Addressing these gaps through enhanced fieldwork and model refinement will significantly improve our ability to predict and manage SPM dynamics, which is critical for sustainable aquatic ecosystem management in an era of rapid environmental change. Full article
(This article belongs to the Section Water Erosion and Sediment Transport)
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<p>Sources, fate, and transport of flocs with heterogeneous composition.</p>
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<p>Schematic diagram of the biogeochemical cycle of carbonaceous materials mediated by flocculation with heterogeneous components in water and benthic environments.</p>
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<p>Schematic diagram of satellite-, aircraft-, and UAV-based remote sensing, and measurable spectral bands of satellites in operation [<a href="#B96-water-16-03613" class="html-bibr">96</a>].</p>
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<p>Basic structure for quantification of (<b>a</b>) total suspended matter (TSM), (<b>b</b>) Chlorophyll-a, and (<b>c</b>) bed load flux using the machine learning algorithms [<a href="#B20-water-16-03613" class="html-bibr">20</a>,<a href="#B115-water-16-03613" class="html-bibr">115</a>,<a href="#B118-water-16-03613" class="html-bibr">118</a>].</p>
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<p>Conceptual schematic of dual frequency echosounder on fluid mud detection with high-frequency (180–220 kHz) and low-frequency (15–38 kHz) ranges [<a href="#B129-water-16-03613" class="html-bibr">129</a>].</p>
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<p>Comparison of (<b>a</b>) single−class population balance equation, (<b>b</b>) two−class population balance equation, (<b>c</b>) three−class population balance equation, and (<b>d</b>) multi−class population balance equation mode [<a href="#B32-water-16-03613" class="html-bibr">32</a>,<a href="#B35-water-16-03613" class="html-bibr">35</a>,<a href="#B145-water-16-03613" class="html-bibr">145</a>,<a href="#B146-water-16-03613" class="html-bibr">146</a>].</p>
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18 pages, 832 KiB  
Article
Monetizing Co-Benefits of Nature-Based Sanitation-Constructed Wetlands Using Contingent Valuation Method—Jordan as a Case Study
by Ahmed M. N. Masoud, Amani Alfarra and Sabrina Sorlini
Water 2024, 16(24), 3612; https://doi.org/10.3390/w16243612 (registering DOI) - 15 Dec 2024
Viewed by 383
Abstract
Parallel to the growing evidence about the efficiency of Nature-based Solutions (NbS) in sanitation, there is a growing need to highlight the co-benefits of these solutions compared to conventional alternatives. This study focuses on economically valuing these co-benefits, with constructed wetlands (CWs) examined [...] Read more.
Parallel to the growing evidence about the efficiency of Nature-based Solutions (NbS) in sanitation, there is a growing need to highlight the co-benefits of these solutions compared to conventional alternatives. This study focuses on economically valuing these co-benefits, with constructed wetlands (CWs) examined as a sanitation solution. The contingent valuation (CV) method has been utilized for this purpose, measuring people’s willingness to pay (WTP) and willingness to accept (WTA) CWs as a sanitation solution. Jordan has been selected as a case study due to the country’s preference for sustainable, cost-efficient solutions. By utilizing extended questionnaires at the stakeholder and community levels, this research aims to identify gaps between these groups’ perspectives on CWs. Additionally, this study investigates the main factors affecting communities’ WTP and WTA. The collected data were analyzed using descriptive statistics for the responses, followed by the CV method, and regression analysis to understand the main factors affecting WTP and WTA. The results are intended to guide decision-makers in developing programs that align with community preferences and address gaps in the acceptance of NbS-CWs. The main results found that while stakeholders have concerns about people’s WTA CWs, the community survey revealed that people prefer CWs over conventional solutions. The findings revealed that 78.9% of respondents were willing to accept (WTA) CWs to treat wastewater in their town, but only 33% WTA having CW near their households. Meanwhile, 53.2% were willing to pay (WTP) for CWs in general, while 80.7% are willing to accept (WTP) using CWs to treat greywater at the household level and 56.9% of the respondents are WTP for that. Full article
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<p>The geographical distributions of the respondents (percentages from the total respondents).</p>
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<p>WTA having CWs to treat wastewater near household.</p>
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<p>WTA having CWs to treat greywater at household.</p>
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16 pages, 2817 KiB  
Article
Optimizing Chemical Oxygen Demand Prediction in Spectroscopy Through Hybrid Feature Engineering and Regression-Based Similarity Analysis
by Chenjie Jia, Zhicheng Zhou, Jiehui Li, Jiankang Ma and Xinming Ji
Water 2024, 16(24), 3611; https://doi.org/10.3390/w16243611 (registering DOI) - 15 Dec 2024
Viewed by 264
Abstract
This paper presents a hybrid feature extraction and regression-based machine learning approach for predicting COD concentrations in water samples using spectral data. The method integrates SK-Best and FA to tackle high dimensionality and information redundancy in small datasets. SK-Best identifies key absorbance features, [...] Read more.
This paper presents a hybrid feature extraction and regression-based machine learning approach for predicting COD concentrations in water samples using spectral data. The method integrates SK-Best and FA to tackle high dimensionality and information redundancy in small datasets. SK-Best identifies key absorbance features, enhancing predictive reliability, while FA reduces dimensionality and extracts valuable information for similarity prediction. The combination of SK-Best, FA, and Linear Regression achieves strong prediction performance (R2 ~ 0.87, MAE = 0.23), demonstrating interpretability, flexibility, and robustness in small datasets. This approach offers a promising solution for real-time water quality monitoring and will be further optimized for broader applications. Full article
17 pages, 3261 KiB  
Article
Characteristics of Suspended Solid Responses to Forest Thinning in Steep Small Headwater Catchments in Coniferous Forest
by Honggeun Lim, Qiwen Li, Byoungki Choi, Hyung Tae Choi and Sooyoun Nam
Water 2024, 16(24), 3610; https://doi.org/10.3390/w16243610 (registering DOI) - 15 Dec 2024
Viewed by 305
Abstract
We examined the responses of suspended solids to forest thinning in steep small headwater catchments, PT (0.8 ha) and PR (0.7 ha), that drain a Korean pine (Pinus koraiensis) plantation forest. Based on a paired-catchment design, the relationship between [...] Read more.
We examined the responses of suspended solids to forest thinning in steep small headwater catchments, PT (0.8 ha) and PR (0.7 ha), that drain a Korean pine (Pinus koraiensis) plantation forest. Based on a paired-catchment design, the relationship between total suspended solids (TSS) and the time differential of water runoff (dQ/dt) indicated a difference in the characteristics of TSS in the rising and falling stages within the initial two years after forest thinning. The relatively high initial TSS responded to the concentration-based first flush criterion in the early stage of the rainfall event concentrated in this initial period after the thinning. The rate of TSS event loads in the PT catchment was 4.3-fold greater than that in the PR catchment within the initial two years after forest thinning. This was induced by the low disturbance of soil surface by forest workers using chainsaws and non-heavy machinery. Three years later, the TSS event loads in the PT catchment appeared to decrease due to trapping and settling by protective vegetation. Therefore, mitigating accelerated TSS events during forest thinning requires appropriate site-specific land preparation, particularly for improving stream water quality in forested catchments. Full article
(This article belongs to the Special Issue Non-Point Source Pollution and Water Resource Protection)
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<p>Location of the study site and monitoring station in forested headwater catchments. The photos show forest thinning operations using chainsaws and non-heavy machinery in the P<sub>T</sub> catchment during the thinning period. Vertical distribution and crown density in the P<sub>T</sub> and P<sub>R</sub> catchments are shown as well.</p>
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<p>Event characteristics of (<b>a</b>) precipitation, (<b>b</b>) total runoff, and (<b>c</b>) mean of total suspended solids (TSS) in P<sub>T</sub> and P<sub>R</sub> catchments during observed 18 rainfall events from 2017 to 2021.</p>
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<p>Time variable mean of the normalized difference vegetation index (NDVI) and total runoff mean of total suspended solids (TSS).</p>
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<p>Total suspended solids (TSS) responses and changes in runoff during selected rainfall events, (<b>a</b>) one year after thinning (27–28 July 2017) and (<b>b</b>) four years after thinning (2–3 October 2019). API<sub>7</sub> and API<sub>30</sub> indicate 7- and 30-day antecedent precipitation indices.</p>
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<p>Relationships between the differential of water runoff (<span class="html-italic">dQ</span>/<span class="html-italic">dt</span>) and (<b>a</b>) runoff and (<b>b</b>) total suspended solids (TSS) in the P<sub>T</sub> (cross) and P<sub>R</sub> (open circle) catchments in different years after forest thinning.</p>
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<p>Cumulative load ratio for total suspended solids (TSS) between the (<b>a</b>) R<sub>R</sub> and (<b>b</b>) P<sub>T</sub> catchments after forest thinning.</p>
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<p>Box plots of the event mean concentration (EMC) in total suspended solids (TSS) for the P<sub>T</sub> and P<sub>R</sub> catchments (<b>a</b>) within the initial two years and (<b>b</b>) from three years after forest thinning onward.</p>
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<p>Relationship between total suspended solids (TSS) event loads from the P<sub>R</sub> and P<sub>T</sub> catchments after forest thinning. Thick and broken lines were calculated using regression analysis within initial two years and three years after forest thinning onward.</p>
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<p>Rate of total suspended solids (TSS) event loads from the P<sub>R</sub> to P<sub>T</sub> catchments during observed 18 rainfall events from 2017 to 2021.</p>
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16 pages, 6401 KiB  
Article
Estimation of Water Interception of Winter Wheat Canopy Under Sprinkler Irrigation Using UAV Image Data
by Xueqing Zhou, Haijun Liu and Lun Li
Water 2024, 16(24), 3609; https://doi.org/10.3390/w16243609 (registering DOI) - 15 Dec 2024
Viewed by 295
Abstract
Canopy water interception is a key parameter to study the hydrological cycle, water utilization efficiency, and energy balance in terrestrial ecosystems. Especially in sprinkler-irrigated farmlands, the canopy interception further influences field energy distribution and microclimate, then plant transpiration and photosynthesis, and finally crop [...] Read more.
Canopy water interception is a key parameter to study the hydrological cycle, water utilization efficiency, and energy balance in terrestrial ecosystems. Especially in sprinkler-irrigated farmlands, the canopy interception further influences field energy distribution and microclimate, then plant transpiration and photosynthesis, and finally crop yield and water productivity. To reduce the field damage and increase measurement accuracy under traditional canopy water interception measurement, UAVs equipped with multispectral cameras were used to extract in situ crop canopy information. Based on the correlation coefficient (r), vegetative indices that are sensitive to canopy interception were screened out and then used to develop canopy interception models using linear regression (LR), random forest (RF), and back propagation neural network (BPNN) methods, and lastly these models were evaluated by root mean square error (RMSE) and mean relative error (MRE). Results show the canopy water interception is first closely related to relative normalized difference vegetation index (R△NDVI) with r of 0.76. The first seven indices with r from high to low are R△NDVI, reflectance values of the blue band (Blue), reflectance values of the near-infrared band (Nir), three-band gradient difference vegetation index (TGDVI), difference vegetation index (DVI), normalized difference red edge index (NDRE), and soil-adjusted vegetation index (SAVI) were chosen to develop canopy interception models. All the developed linear regression models based on three indices (R△NDVI, Blue, and NDRE), the RF model, and the BPNN model performed well in canopy water interception estimation (r: 0.53–0.76, RMSE: 0.18–0.27 mm, MRE: 21–27%) when the interception is less than 1.4 mm. The three methods underestimate the canopy interception by 18–32% when interception is higher than 1.4 mm, which could be due to the saturation of NDVI when leaf area index is higher than 4.0. Because linear regression is easy to perform, then the linear regression method with NDVI is recommended for canopy interception estimation of sprinkler-irrigated winter wheat. The proposed linear regression method and the R△NDVI index can further be used to estimate the canopy water interception of other plants as well as forest canopy. Full article
(This article belongs to the Special Issue Agricultural Water-Land-Plant System Engineering)
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<p>Map of experimental location and experimental field in this study.</p>
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<p>Heat map of correlation analysis between vegetation indices and canopy water interception. Note: * indicates the correlation coefficient between the two indices is significant at 0.05 level; ** indicates the relationship is significant at 0.01 level.</p>
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<p>Performance of linear regression models using unary and multiple vegetative indices. Panel (<b>a</b>) represents the linear model based on R<sub>△NDVI</sub> (model 7 in <a href="#water-16-03609-t003" class="html-table">Table 3</a>); (<b>b</b>) represents the model based on R<sub>△NDVI</sub> and Blue (model 8 in <a href="#water-16-03609-t003" class="html-table">Table 3</a>); (<b>c</b>) represents model based on R<sub>△NDVI</sub>, Blue, and NDRE (model 11 in <a href="#water-16-03609-t003" class="html-table">Table 3</a>).</p>
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<p>The estimated and measured canopy interceptions by RF model in the model developing and calibrating processes.</p>
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<p>The estimated and measured canopy interceptions by BP neural network model in the model developing and calibrating processes.</p>
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<p>The relationship between normalized difference vegetation index (NDVI) and leaf area index (LAI) in winter wheat.</p>
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16 pages, 4094 KiB  
Article
Study of the Biogas Ebullition from Lacustrine Carbonate Enriched and Black Silt Bottom Sediments
by Evaldas Maceika, Laima Kazakevičiūtė-Jakučiūnienė, Zita Žukauskaitė, Nina Prokopčiuk, Marina Konstantinova, Vadimas Dudoitis and Nikolay Tarasiuk
Water 2024, 16(24), 3608; https://doi.org/10.3390/w16243608 (registering DOI) - 15 Dec 2024
Viewed by 312
Abstract
The greenhouse effect, which is also promoted by naturally occurring biogas ebullition fluxes (released via bubbles), generated by the decomposition of organic matter in carbonate-enriched and black silt sediments, has been analyzed. This study is based on results obtained using passive gas collectors [...] Read more.
The greenhouse effect, which is also promoted by naturally occurring biogas ebullition fluxes (released via bubbles), generated by the decomposition of organic matter in carbonate-enriched and black silt sediments, has been analyzed. This study is based on results obtained using passive gas collectors at different parts of eutrophic Lake Juodis, located in a temperate climate zone in the vicinity of Vilnius (Lithuania). The measured annual biogas (containing about 60% of biomethane) ebullition fluxes from carbonate-enriched sediments and black silt sediments were 16.9–23.0 L/(m2∙y) and 38.5–43.2 L/(m2∙y), respectively. This indicates that the gas fluxes from carbonate sediments were almost twice as low as those from black silt sediments. Oxygen, produced by the photosynthetic activity of green algae in the near-surface water and sediments, helps to retain carbonates in the sediments by preventing their dissolution. In turn, the calcite coating on sediment particles partially preserves organic matter from decomposition, reducing the effective thickness of the sediment layer generating biogas. The characteristic vertical distribution profile of 137Cs activity, with sharp peaks in sediments, suggests that generated biogas bubbles move to the surface of the sediments forming vertical channels by pushing sediment particles asides without noticeably mixing them vertically. This examination showed that factors such as abundance of carbonates in the sediments may result in a significant reduction in biogas generation and emissions from the lake sediments. Full article
(This article belongs to the Section Water Quality and Contamination)
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<p>Scheme of the biogas (methane) sampling sites (N1–N13) (●) using the “Jellyfish” apparatus on 8 August 2003 in Lake Juodis and the location of the northern (×) and southern stations (+) on a shallow bottom terrace. Carbonate sediment N1 and N2 (●) were sampled near the northern station (×); black silt sediment N3 (●) was sampled near the southern station (+); inflow and outflow of the brook (←).</p>
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<p>Microscopic photographs of the extracted sediment samples: (<b>a</b>) black silt, typically containing a large amount of decomposing organic matter and trapped biogas bubbles; (<b>b</b>) carbonate sediments, containing remnants of green algae.</p>
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<p>Vertical profiles of oxygen concentrations (mg/L) in the northern part of the lake in the green algae area (northern station) on 19 August 2003 (<b>a</b>) (bottom depth~122 cm), 3 November 2003 (<b>b</b>) (bottom depth~120 cm), and 16 March 2004 (<b>c</b>) (bottom depth~115 cm, the transparent ice thickness of ~32 cm).</p>
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<p>Vertical profile of oxygen concentrations (mg/L) in the northern part of the lake in the area of black silt sediments (southern station) on 11 August 2004 (<b>a</b>) (bottom depth~141 cm) and 13 October 2004 (<b>b</b>) (bottom depth~147 cm).</p>
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<p>Vertical profiles of <sup>137</sup>Cs activity concentration (<b>a</b>) and sediment density (<b>b</b>) in sample N1 of bottom sediments (rich in carbonate deposits) collected on 16 July 2003 near the northern sampling station (×) at a depth of 110 cm.</p>
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<p>Vertical profiles of <sup>137</sup>Cs activity concentration (<b>a</b>) and sediment density (<b>b</b>) in the sample N2 of bottom sediments (rich in carbonate deposits) collected on 16 July 2003 near the northern sampling station (×) at a depth of 120 cm.</p>
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<p>Vertical profiles of <sup>137</sup>Cs activity concentration (<b>a</b>) and sediment density (<b>b</b>) in the sample of black silt deposits (N3) taken on 29 August 2003 near the southern sampling station (+) at a depth of 140 cm.</p>
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<p>Biogas ebullition flux (L/m<sup>2</sup>∙s) from 18 September 2005 to 19 May 2007 (<b>a</b>) and from 8 October 2008 to 6 October 2010 (<b>b</b>) at the northern station (carbonate sediments).</p>
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<p>Biogas ebullition flux (L/m<sup>2</sup>∙s) from 18 September 2005 to 6 August 2007 (<b>a</b>) and from 8 October 2008 to 19 October 2010 (<b>b</b>) at the southern station (black silt sediments).</p>
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16 pages, 2554 KiB  
Article
Revealing the Adverse Potential of Six SARS-CoV-2 Antivirals by Aliivibrio fischeri Assay: Toxicity Analysis of Single Agent Solutions and Binary Mixtures
by Viktorija Martinjak, Martina Miloloža, Marinko Markić, Lidija Furač, Matija Cvetnić, Tomislav Bolanča, Dajana Kučić Grgić and Šime Ukić
Water 2024, 16(24), 3607; https://doi.org/10.3390/w16243607 (registering DOI) - 15 Dec 2024
Viewed by 537
Abstract
The COVID-19 pandemic has intensified the development of new antiviral agents specifically intended for the SARS-CoV-2 virus, but has also increased the use of some already known antiviral agents originally intended for other viruses. Although the pandemic has ended, the SARS-CoV-2 virus is [...] Read more.
The COVID-19 pandemic has intensified the development of new antiviral agents specifically intended for the SARS-CoV-2 virus, but has also increased the use of some already known antiviral agents originally intended for other viruses. Although the pandemic has ended, the SARS-CoV-2 virus is expected to be present in the human population forever, as is the case with the influenza virus, for example. Such a scenario guarantees the continued use of SARS-CoV-2 antivirals and, accordingly, their continued release into the environment. Unfortunately, there is little or no information on the adverse potential of most of these antiviral agents. In this study, the acute toxicity of six antiviral agents used in the treatment of SARS-CoV-2 infections was determined. These are atazanavir, ribavirin, emtricitabine, nirmatrelvir, sofosbuvir and oseltamivir, sorted according to their toxicity, starting with the most toxic agent. Toxicity was determined using the marine bacterium Aliivibrio fischeri according to the ISO 11348-1:2007 standard. In addition to the toxicities of the individual antiviral solutions, the toxicities of binary antiviral mixtures were also determined. By comparing the experimentally determined toxicities of the mixtures with the values estimated by the concentration addition model and the independent action model, we analyzed the mode of joint toxic activity of these antiviral agents. Additive behavior was observed for most binary combinations. The combination of nirmatrelvir and sofosbuvir led to an antagonistic deviation from the concentration addition model, while a synergistic deviation was observed for the combinations of emtricitabine with atazanavir and with nirmatrelvir, as well as for the combinations of ribavirin with atazanavir, oseltamivir and sofosbuvir. All tested binary combinations showed a synergistic deviation from the independent action model. Full article
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<p>Chemical structures of: (<b>A</b>) atazanavir, (<b>B</b>) emtricitabine, (<b>C</b>) nirmatrelvir, (<b>D</b>) oseltamivir, (<b>E</b>) ribavirin and (<b>F</b>) sofosbuvir.</p>
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<p>Isobolograms of binary mixtures of antivirals. Comparison of experimentally determined joint toxicity (circles) and additive behavior (solid lines). Different colors represent different binary mixtures, i.e., the mixtures containing different ratios of the individual antiviral solutions: MIX 1 (75:25; blue circle), MIX 2 (50:50, red circle) and MIX 3 (25:75, green circle).</p>
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<p>Comparison between the predicted and experimentally determined toxicity values for the mixtures of (<b>A</b>) nirmatrelvir and sofosbuvir, and (<b>B</b>) oseltamivir and sofosbuvir. The cases correspond to the concentration addition model (red color) and the independent action model (blue color). The straight line is the <span class="html-italic">y</span> = <span class="html-italic">x</span> line, which represents the ideal scenario where the predicted values agree with the experimentally obtained values.</p>
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<p>Correlation between toxicity and (<b>A</b>) the logP value, and (<b>B</b>) molar mass, for atazanavir, nirmatrelvir, oseltamivir and sofosbuvir (blue circles). The orange circles represent the highly hydrophilic antiviral agents emtricitabine and ribavirin, which were excluded from the regression analysis.</p>
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17 pages, 4357 KiB  
Review
Nature-Based Solutions (NbS) for Flood Management in Malaysia
by Haziq Sarhan Bin Rosmadi, Minhaz Farid Ahmed, Mazlin Bin Mokhtar, Bijay Halder and Miklas Scholz
Water 2024, 16(24), 3606; https://doi.org/10.3390/w16243606 (registering DOI) - 15 Dec 2024
Viewed by 295
Abstract
Flash floods are a concerning social issue that affect urban areas all over the world. Flash floods can disrupt vital services, damage infrastructure, have socio-economic impacts on the earth’s surface, and significantly impact the community near the water body. Household and commercial damage, [...] Read more.
Flash floods are a concerning social issue that affect urban areas all over the world. Flash floods can disrupt vital services, damage infrastructure, have socio-economic impacts on the earth’s surface, and significantly impact the community near the water body. Household and commercial damage, physical health issues from contaminated floodwater, mental health issues including post-traumatic stress disorder, and even fatalities are some of these common effects. Additionally, it is anticipated that climate change, continuous population growth, and urbanisation will increase flood events and flood risk exposure. Nature-based solutions (NbS) for flood management that lower flood risks include sustainable, economical methods that improve biodiversity, ecosystem resilience, and community well-being. This in-depth study analyses research and literature that previous researchers conducted related to flood management around ASEAN countries, as all these countries are closely located and share similarities in climate and temperature. This survey focuses on identifying the most suitable and effective NbS to overcome the problem and appropriate non-structural measures to support it in solving the flood problem in Malaysia. NbS provide a multi-benefit approach by improving ecosystem resilience, cutting costs, and offering co-benefits, including biodiversity conservation and better water quality, in contrast to conventional methods that put infrastructure before environmental sustainability. This survey also looks at the weaknesses in the existing flood management system and provides recommendations to overcome these problems. Additionally, this survey offers practical policy suggestions to help incorporate NbS into regional and national flood control frameworks, guaranteeing that the solutions are not only socially just but also ecologically sound. Full article
(This article belongs to the Special Issue Recent Advances in Flood Risk Analysis and Management Practice)
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<p>Different flood management approaches and benefits of NbS implementation in flood management.</p>
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<p>The PRISMA 2020 statement: an updated guideline for reporting systematic reviews (based on [<a href="#B24-water-16-03606" class="html-bibr">24</a>]).</p>
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<p>Floods and Malaysia, previous study and literature keywords based on Scopus. 271 papers were identified in Malaysia but were limited to the NbS study.</p>
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<p>Researchers from different countries are involved in flood management studies in Malaysia. 271 papers were identified in Malaysia but were limited to the NbS study.</p>
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17 pages, 8422 KiB  
Article
A New Procedure for Determining Monthly Reservoir Storage Zones to Ensure Reliable Hourly Hydropower Supply
by Shuangquan Liu, Jingzhen Luo, Kaixiang Fu, Huixian Li, Guoyuan Qian, Wang Xia and Jinwen Wang
Water 2024, 16(24), 3605; https://doi.org/10.3390/w16243605 (registering DOI) - 14 Dec 2024
Viewed by 400
Abstract
The uncertainty of natural inflows and market behavior challenges ensuring a reliable power balance in hydropower-dominated electricity markets. This study proposes a novel framework integrating hourly load balancing on typical days into a monthly scheduling model solved with Gurobi11.0.1 to evaluate demand-met reliability [...] Read more.
The uncertainty of natural inflows and market behavior challenges ensuring a reliable power balance in hydropower-dominated electricity markets. This study proposes a novel framework integrating hourly load balancing on typical days into a monthly scheduling model solved with Gurobi11.0.1 to evaluate demand-met reliability across storage and inflow states. By employing total storage as a system state to reduce dimensional complexity and simulating future runoff scenarios based on current inflows, the method performs multi-year statistical simulations to assess reliability over the following year. Applied to a system of 39 hydropower reservoirs in China, the case studies of present models and procedures suggest: (1) controlling reservoir storage levels during the dry season is crucial for ensuring the power demand-met rate in the following year, with May being the most critical month; (2) the power demand-met rate does not monotonically increase with higher storage levels—there is an optimal storage level that maximizes the demand-met rate; and (3) June and October offer the greatest flexibility in storage adjustment to achieve the highest demand-met reliability. Full article
(This article belongs to the Special Issue Research Status of Operation and Management of Hydropower Station)
26 pages, 14322 KiB  
Article
Effects of War-Related Human Activities on Microalgae and Macrophytes in Freshwater Ecosystems: A Case Study of the Irpin River Basin, Ukraine
by Inna Nezbrytska, Olena Bilous, Tetyana Sereda, Natalia Ivanova, Maryna Pohorielova, Tetyana Shevchenko, Serhii Dubniak, Olena Lietytska, Vladyslav Zhezherya, Oleksandr Polishchuk, Taras Kazantsev, Mykola Prychepa, Yulia Kovalenko and Sergyi Afanasyev
Water 2024, 16(24), 3604; https://doi.org/10.3390/w16243604 (registering DOI) - 14 Dec 2024
Viewed by 507
Abstract
Throughout the world, river basins are directly or indirectly affected by human activities, reducing local and global biodiversity and preventing the ecosystem from properly functioning. Our research focused on the Irpin River basin (Ukraine), whose water bodies have experienced various impacts due to [...] Read more.
Throughout the world, river basins are directly or indirectly affected by human activities, reducing local and global biodiversity and preventing the ecosystem from properly functioning. Our research focused on the Irpin River basin (Ukraine), whose water bodies have experienced various impacts due to human activities, including the unexpected extremes caused by military operations in the catchment area: long-term flooding, disturbance of free flow, significant water level fluctuations, etc. The study hypothesized that the primary factors determining the structural and spatial distribution of quantitative indicators of microalgae and aquatic macrophytes are the result of various hydromorphological changes, that lead to changes in the physical and chemical parameters of the aquatic environment. Very high values of chlorophyll a in the water column (59–106 µg · L−1), an increase in the abundance (number of cells) and biomass of algae (due to the predominance of certain groups in the transformed sections), as well as saprobic index were recorded in the sections of the Irpin River basin that underwent significant hydromorphological changes. Our results revealed a strong correlation between phytoplanktonic (in the water column) chlorophyll a levels and water temperature (r = 0.76, p < 0.001), as well as organic phosphorus and polyphosphate concentrations (r = 0.61, p < 0.01). ANOVA and Monte Carlo permutation tests in a Canonical Correspondence Analysis (CCA) showed that the abundance of different divisions of phytoplankton and phytobenthos were significantly and similarly related to several environmental variables. We observed a positive correlation between the number of cyanobacteria and the concentration of ammonium nitrogen, nitrites, and phosphorus compounds. An increase in dissolved organic matter in the water can explain the increase in the biomass of Dinoflagellata and Euglenophyta. Species richness and the cover values of the macrophytes also clearly reflected changes in vegetation activity in sections of the Irpin River caused by hydromorphological changes. The results indicated that long-term flooding had the most negative impact on macrophyte communities. At some sites, the impact was so severe that the number of macrophyte species was very low. The total number of macrophyte species showed a significant negative correlation with total suspended solids (r = −0.51, p < 0.05) and phytoplankton chlorophyll a concentration (r = −0.73, p < 0.001). Our results provide a scientific basis for predicting changes in riverine microalgal and aquatic macrophyte communities due to extreme hydrological events. Full article
(This article belongs to the Special Issue Biodiversity of Freshwater Ecosystems: Monitoring and Conservation)
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<p>The catchment area of the Irpin River with the sampling sites: 1—village Khodorkiv; 2—downstream the river, village Khodorkiv; 3—in town Kornyn, reservoir; 4—village Didivschyna; 5—before village Yaroshivka; 6—village Chornohorodka; 7—village Dzvinkove; 8—village Knyazhychi; 9—village Romanivka; 10—village Chervone (500 m away from village); 11—village Demidiv (500 m far from village). Some of the sites were positioned on the tributaries: 12—river Unava, village; 13—river Unava, village Kvitneve; 14—river Zharka, village Didivshchyna; 15—river Lupa, village Bishiv; 16—river Horenka, town Gostomel (600 m away from town, downstream); 17—river Rokach, town Gostomel (900 m away from town, downstream).</p>
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<p>An overflow of the Irpin River (with a focus on a dam near the village of Kozarovychi) at different times due to war actions in Ukraine. (<b>A</b>) 10 April 2021; (<b>B</b>) 23 March 2022; (<b>C</b>) 21 March 2023. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>. The colors are provided by a combination of band 8 (near infrared), band 12 (infrared), and band 2 (blue), where water sections are clearly visible as dark areas.</p>
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<p>Dynamics of the concentration of chlorophyll <span class="html-italic">a</span> in the waters of the Irpin River basin. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>.</p>
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<p>The similarity tree of the composition of the algal species (presence/absence, in terms of the Sørensen index) for the Irpin River basin. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>.</p>
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<p>The composition of the algal species, grouped according to phyla, for each site in the Irpin River basin. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>. (<b>a</b>)—number of taxa, (<b>b</b>)—percentage of total number of taxa.</p>
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<p>The composition of the algal species, grouped according to phyla, for each site in the Irpin River basin. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>. (<b>a</b>)—number of taxa, (<b>b</b>)—percentage of total number of taxa.</p>
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<p>The species composition (<b>a</b>) and habitat preferences (<b>b</b>) of the total algal assemblages in the Irpin River basin. (<b>a</b>) Total = both communities; pl—phytoplankton; pb—phytobenthos. (<b>b</b>) P—planktonic; P–B—plankton–benthic; B—benthic; Ep—epiphytes; S—soil. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>.</p>
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<p>The species composition (<b>a</b>) and habitat preferences (<b>b</b>) of the total algal assemblages in the Irpin River basin. (<b>a</b>) Total = both communities; pl—phytoplankton; pb—phytobenthos. (<b>b</b>) P—planktonic; P–B—plankton–benthic; B—benthic; Ep—epiphytes; S—soil. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>.</p>
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<p>Abundance (total number of cells) of phytoplankton (<b>a</b>,<b>b</b>) and phytobenthos (<b>c</b>,<b>d</b>) for the Irpin River basin. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>.</p>
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<p>Abundance (total number of cells) of phytoplankton (<b>a</b>,<b>b</b>) and phytobenthos (<b>c</b>,<b>d</b>) for the Irpin River basin. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>.</p>
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<p>Biomass of phytoplankton (<b>a</b>,<b>b</b>) and phytobenthos (<b>c</b>,<b>d</b>) in the Irpin River basin. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>.</p>
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<p>Biomass of phytoplankton (<b>a</b>,<b>b</b>) and phytobenthos (<b>c</b>,<b>d</b>) in the Irpin River basin. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>.</p>
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<p>The saprobic index values calculated for the abundance (SN) and biomass (SB) of the phytoplankton (<b>a</b>) and phytobenthos (<b>b</b>) for the Irpin River basin. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>.</p>
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<p>CCA ordination diagram of site scores, phytoplankton, and phytobenthos community structure parameters (abundance/number of cells), and selected environmental variables (represented by arrows) in the Irpin River basin. Only the significant explanatory environmental variables (<span class="html-italic">p</span> &lt; 0.05) are shown. Sites that could be affected by military actions are marked in bold. The abbreviations are as follows: <span class="html-italic">Chlorophyta</span> –Chl.; <span class="html-italic">Dinoflagellata</span>—Dino.; <span class="html-italic">Heterokontophyta</span>—Heter.; <span class="html-italic">Euglenophyta</span>—Eugl.; <span class="html-italic">Cryptisa</span>—Cry.; <span class="html-italic">Cyanobacteria</span>—Cyano.; <span class="html-italic">Charophyta</span>—Charo. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>.</p>
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<p>CCA ordination diagram of site scores, macrophyte community structure parameters and selected environmental variables (represented by arrows) in the Irpin River catchment. Only significant environmental variables (<span class="html-italic">p</span> &lt; 0.05) are shown. Sites that could be affected by the war are marked in bold. Numbers correspond to the sampling sites and are identical to those in <a href="#water-16-03604-f001" class="html-fig">Figure 1</a>.</p>
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22 pages, 5263 KiB  
Article
Determination of Heavy Metals and Hemato-Biochemical Profiling of Bagre marinus and Bagarius bagarius in Jhelum River
by Muneeba Shaheen, Sana Ullah, Muhammad Bilal, Ahmed Muneeb, Begum Yurdakok-Dikmen and Caterina Faggio
Water 2024, 16(24), 3603; https://doi.org/10.3390/w16243603 (registering DOI) - 14 Dec 2024
Viewed by 263
Abstract
Heavy metals enter river basins through industrial effluents, agricultural wastes, surface run-offs, and other human activities, negatively impacting aquatic and terrestrial life by bioaccumulating in the food chain. This problem is on a continuous rise in under-developed and developing countries, such as in [...] Read more.
Heavy metals enter river basins through industrial effluents, agricultural wastes, surface run-offs, and other human activities, negatively impacting aquatic and terrestrial life by bioaccumulating in the food chain. This problem is on a continuous rise in under-developed and developing countries, such as in Pakistan. Therefore, the current study was aimed to determine concentrations of heavy metals, essential trace elements, and macrominerals (Zn, Pb, Ni, Mn, Mg, Fe, Cu, Cr, Co, Cd, Ca, and As) in the water, sediments, and tissues (gills, liver, and muscles) of Bagarius bagarius and Bagre marinus in the Jhelum River, Pakistan. The hematological and biochemical profiles of these fish across two sampling sites (Jhelum Bridge Khushab, upstream, and Langarwala Pull—downstream) were also evaluated. Results showed greater bioaccumulation of heavy metals in fish downstream, correlating with higher concentrations of these metals in water and sediments downstream. In the case of B. marinus, the highest concentration observed was 16.59 mg/g (Ca), and the lowest concentration was 9.51 mg/g (Fe). In the case of B. bagarius, the highest concentration observed was 17.47 mg/g (Ca), and the lowest concentration was 7.95 mg/g (Mg). Increased activities of alkaline phosphatase (ALP), alanine aminotransferase (ALT), aspartate aminotransferase (AST), and lactate dehydrogenase (LDH) were observed downstream. Hematological changes included increased white blood cells (WBCs) and decreased red blood cells (RBCs), lymphocytes, hemoglobin (Hb), platelets (Plt), and hematocrit (Hct). A significant correlation was observed among heavy metals across the water, sediment, and different tissues of B. marinus and B. bagarius. Moreover, principal component analysis (PCA) for both species along both sampling sites illustrated the relationship between fish tissues and metals. The current study concluded that the fish accumulated a significantly higher concentration of heavy metals downstream, which might be linked with dumping of the domestic wastes and industrial and agricultural runoff, adversely affecting both fish and human health. Full article
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<p>Summary of the preparation of samples for analysis.</p>
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<p>Heavy metal concentrations in (<b>A</b>) water and (<b>B</b>) sediment; data presented as Mean ± SE; significant difference among sites is represented by asterisks (two-sample <span class="html-italic">t</span>-test, <span class="html-italic">p</span> &lt; 0.05 = *, <span class="html-italic">p</span> &lt; 0.01 = **, and <span class="html-italic">p</span> &lt; 0.001 = ***). Heavy metal concentrations in tissues of (<b>C</b>) <span class="html-italic">B. marinus</span> (upstream), (<b>D</b>) <span class="html-italic">B. marinus</span> (downstream), (<b>E</b>). <span class="html-italic">B. bagarius</span> (upstream), and (<b>F</b>) <span class="html-italic">B. bagarius</span> (downstream); data are given as Mean ± SE and superscripted letters on bars show significance difference at <span class="html-italic">p</span> &lt; 0.05 (ANOVA followed by LSD).</p>
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<p>Level of heavy metals in the tissues of <span class="html-italic">Bagre marinus</span> and <span class="html-italic">Bagarius bagarius</span>. (<b>A</b>) Liver of <span class="html-italic">B. marinus</span>, (<b>B</b>) liver of <span class="html-italic">B. bagarius</span>, (<b>C</b>) gills of <span class="html-italic">B. marinus</span>, (<b>D</b>) gills of <span class="html-italic">B. bagarius</span>, (<b>E</b>) muscles of <span class="html-italic">B. marinus</span>, and (<b>F</b>) muscles of <span class="html-italic">B. bagarius</span>. Data presented as Mean ± SE. Significant difference among sites is represented by an asterisks (two-sample <span class="html-italic">t</span>-test, <span class="html-italic">p</span> &lt; 0.05 = *, <span class="html-italic">p</span> &lt; 0.01 = **, and <span class="html-italic">p</span> &lt; 0.001 = ***).</p>
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<p>Hematological profile of <span class="html-italic">Bagre marinus</span> and <span class="html-italic">Bagarius Bagarius</span> from upstream (US) and downstream (DS) of Jhelum River in Khushab District. Data represented as Mean ± SE. Significant difference among sites is represented by asterisks (two-sample <span class="html-italic">t</span>-test, <span class="html-italic">p</span> &lt; 0.05 = *, <span class="html-italic">p</span> &lt; 0.01 = **, and <span class="html-italic">p</span> &lt; 0.001 = ***).</p>
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<p>Serum biochemical profile of <span class="html-italic">Bagre marinus</span> and <span class="html-italic">Bagarius bagarius</span> from upstream (US) and downstream (DS) of Jhelum River in Khushab. (<b>A</b>) Bilirubin for <span class="html-italic">B. marinus</span>, (<b>B</b>) bilirubin for <span class="html-italic">B. bagarius</span>, (<b>C</b>) protein for <span class="html-italic">B. marinus</span>, (<b>D</b>) protein for <span class="html-italic">B. bagarius</span>, (<b>E</b>) enzymes for <span class="html-italic">B. marinus</span>, (<b>F</b>) enzymes for <span class="html-italic">B. bagarius</span>, (<b>G</b>) nitrogenous wastes for <span class="html-italic">B. marinus</span>, (<b>H</b>) nitrogenous wastes for <span class="html-italic">B. bagarius</span>, and (<b>I</b>) LDH for both species. Data presented as Mean ± SE. Significant difference among sites is represented by asterisks (two-sample <span class="html-italic">t</span>-test, <span class="html-italic">p</span> &lt; 0.05 = *, <span class="html-italic">p</span> &lt; 0.01 = ** and <span class="html-italic">p</span> &lt; 0.001 = ***).</p>
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<p>PCA diagrams for <span class="html-italic">Bagre marinus</span> and <span class="html-italic">Bagarius bagarius</span> along upstream and downstream sites of Jhelum River in Khushab District. (<b>A</b>) shows <span class="html-italic">Bagre marinus</span> at upstream, (<b>B</b>) shows <span class="html-italic">Bagre marinus</span> downstream, (<b>C</b>) shows <span class="html-italic">Bagarius bagarius</span> upstream and (<b>D</b>) shows <span class="html-italic">Bagarius bagarius</span> downstream.</p>
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14 pages, 8958 KiB  
Article
Improved Detection of Great Lakes Water Quality Anomalies Using Remote Sensing
by Karl R. Bosse, Robert A. Shuchman, Michael J. Sayers, John Lekki and Roger Tokars
Water 2024, 16(24), 3602; https://doi.org/10.3390/w16243602 (registering DOI) - 14 Dec 2024
Viewed by 251
Abstract
Due to their immense economic and recreational value, the monitoring of Great Lakes water quality is of utmost importance to the region. Historically, this has taken place through a combination of ship-based sampling, buoy measurements, and physical models. However, these approaches have spatial [...] Read more.
Due to their immense economic and recreational value, the monitoring of Great Lakes water quality is of utmost importance to the region. Historically, this has taken place through a combination of ship-based sampling, buoy measurements, and physical models. However, these approaches have spatial and temporal deficiencies which can be improved upon through satellite remote sensing. This study details a new approach for using long time series of satellite remote sensing data to identify historical and near real-time anomalies across a range of data products. Anomalies are traditionally detected as deviations from historical climatologies, typically assuming that there are no long-term trends in the historical data. However, if present, such trends could result in misclassifying ordinary events as anomalous or missing actual anomalies. The new anomaly detection method explicitly accounts for long-term trends and seasonal variability by first decomposing a 10-plus year data record of satellite remote sensing-derived Great Lakes water quality parameters into seasonal, trend, and remainder components. Anomalies were identified as differences between the observed water quality parameter from the model-derived expected value. Normalizing the anomalies to the mean and standard deviation of the full model remainders, the relative anomaly product can be used to compare deviations across parameters and regions. This approach can also be used to forecast the model into the future, allowing for the identification of anomalies in near real time. Multiple case studies are detailed, including examples of a harmful algal bloom in Lake Erie, a sediment plume in Saginaw Bay (Lake Huron), and a phytoplankton bloom in Lake Superior. This new approach would be best suited for use in a water quality dashboard, allowing users (e.g., water quality managers, the research community, and the public) to observe historical and near real-time anomalies. Full article
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<p>Map showing the study area, consisting of all five of the Laurentian Great Lakes.</p>
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<p>Workflow diagram showing the process of getting from individual VIIRS satellite images to 10-day aggregated STL decomposition products.</p>
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<p>Lake-wide average seasonal time series for Lake Erie CHL (panel (<b>A</b>)), Lake Huron SM (panel (<b>B</b>)), and Lake Superior PZD (panel (<b>C</b>)). Each panel shows the annual seasonal patterns as light gray lines, the 11-year mean as a black line, and the 11-year standard deviation in the gray window.</p>
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<p>Lake-wide average time series are shown for the three example parameters: Lake Erie CHL (panels (<b>A</b>–<b>C</b>)), Lake Huron SM (panels (<b>D</b>–<b>F</b>)), and Lake Superior PZD (panels (<b>G</b>–<b>I</b>)). The panels in the left column show the parameter value time series. The panels in the center column show the absolute anomaly (A) time series. The panels in the right column show the relative anomaly (rA) time series.</p>
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<p>Western Lake Erie harmful algal bloom case study from 22 September 2015. Panel (<b>A</b>) shows the VIIRS true color image, with panel (<b>B</b>) showing the CPA-A derived CHL for the image. Panel (<b>C</b>) shows the expected CHL for this date based on the STL decomposition. Panels (<b>D</b>,<b>E</b>) show the absolute and relative CHL anomaly maps, respectively.</p>
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<p>Saginaw Bay sediment plume case study from 21 May 2020. Panel (<b>A</b>) shows the VIIRS true color image, with panel (<b>B</b>) showing the CPA-A derived SM for the image. Panel (<b>C</b>) shows the expected SM for this date based on the STL decomposition. Panels (<b>D</b>,<b>E</b>) show the absolute and relative SM anomaly maps, respectively.</p>
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<p>Lake Superior CHL forecast case study from 2 August 2023. Panel (<b>A</b>) shows the VIIRS true color image, with panel (<b>B</b>) showing the CPA-A derived CHL for the image. Panel (<b>C</b>) shows the expected CHL for this date based on the STL decomposition and forecast. Panels (<b>D</b>,<b>E</b>) show the absolute and relative CHL anomaly maps, respectively.</p>
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17 pages, 2944 KiB  
Article
Efficiency of Cerium Nitrate and Hydrogen Peroxide in Removing Ammonia and Nitrite from Aquaculture Wastewater and Its Impact on Microbial Community Dynamics
by Yu Qiao, Zhongyi Qu, Wenhuan Yang, Zhichao Wang, Ke Li and Weiping Li
Water 2024, 16(24), 3601; https://doi.org/10.3390/w16243601 (registering DOI) - 14 Dec 2024
Viewed by 317
Abstract
Aquaculture wastewater is rich in nutrients such as nitrogen and phosphorus. If discharged directly without treatment, it can cause eutrophication of water bodies and the proliferation of algae. This study explores the treatment of aquaculture wastewater using cerium nitrate and hydrogen peroxide. To [...] Read more.
Aquaculture wastewater is rich in nutrients such as nitrogen and phosphorus. If discharged directly without treatment, it can cause eutrophication of water bodies and the proliferation of algae. This study explores the treatment of aquaculture wastewater using cerium nitrate and hydrogen peroxide. To improve the treatment efficiency of ammonia and nitrite in aquaculture wastewater, a Box–Behnken design with three factors at three levels was used to optimize the process of treating aquaculture wastewater with cerium nitrate and hydrogen peroxide. The optimal process conditions for removing ammonia and nitrite were determined to be a Ce(NO3)3 dosage of 0.18 g/L, an H2O2 reaction concentration of 1.0%, and a reaction time of 30 min. Under the optimal reaction conditions, the degradation rate of ammonia and nitrite can reach 80% or more. Finally, high-throughput sequencing technology was used to explore the impact of cerium nitrate and hydrogen peroxide treatment on microbial community structure and metabolic pathways. The results showed that, at the phylum level, the dominant positions of Actinobacteriota, Proteobacteria, and Bacteroidota were maintained throughout the entire culture period. At the genus level, the relative abundance of the hgcI_clade genus under Actinobacteriota significantly increased, becoming the main dominant genus throughout the culture period. Under the condition of adding cerium nitrate and hydrogen peroxide, the metabolic functions of the microbial community were enhanced. The addition of cerium nitrate and hydrogen peroxide increased the abundance of key nitrogen metabolism genes such as amo, hao, and nap, thereby enhancing the potential nitrification/denitrification capabilities of microorganisms. The combination of cerium nitrate and hydrogen peroxide showed positive effects in the treatment of aquaculture wastewater, providing a new strategy for the green treatment of wastewater. Full article
(This article belongs to the Special Issue Water Quality, Wastewater Treatment and Water Recycling)
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<p>Measured and predicted values of ammonia.</p>
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<p>Measured and predicted values of nitrite.</p>
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<p>Changes in ammonia nitrogen concentration.</p>
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<p>Change in nitrite nitrogen concentration.</p>
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<p>Phylum level microbial community composition.</p>
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<p>Microbial community composition at genus level.</p>
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<p>KEGG tertiary metabolic pathway note.</p>
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<p>Abundance of nitrogen metabolism functional genes.</p>
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17 pages, 6264 KiB  
Article
Linking Water Quality Indicators in Stable Reservoir Ecosystems: Correlation Analysis and Ecohydrological Implications
by Juan Du, Xiao Yang, Peng Xu, Xiang Wan, Pan Wang, Ding Wang, Qi Yang, Qiu Wang and Amar Razzaq
Water 2024, 16(24), 3600; https://doi.org/10.3390/w16243600 (registering DOI) - 14 Dec 2024
Viewed by 372
Abstract
This research was conducted to determine the connections between dissolved oxygen (DO), chemical oxygen demand (COD), permanganate index (CODMn), five-day biochemical oxygen demand (BOD5), and ammonia nitrogen (NH3-H) across five reservoirs of Yunmeng County, China, from January to November [...] Read more.
This research was conducted to determine the connections between dissolved oxygen (DO), chemical oxygen demand (COD), permanganate index (CODMn), five-day biochemical oxygen demand (BOD5), and ammonia nitrogen (NH3-H) across five reservoirs of Yunmeng County, China, from January to November 2022. Each month, water samples were collected and subjected to analysis using standard methods. The samples were collected and analyzed using standard methods: dissolved oxygen was determined using the electrochemical probe method, COD was measured via the rapid digestion spectrophotometric method, CODMn was detected using the potassium permanganate oxidation method, BOD5 was determined using the dilution and inoculation method, and NH3-N was measured by using the Nessler reagent spectrophotometry method. The results confirmed strong positive correlations between COD and CODMn, with different intensities from reservoir to reservoir. More specific and demanding COD parameters were used to estimate the level of oxygen consumption; hence, a more variable correlation strength was observed between BOD5 and the other two parameters. Thus, BOD5 was found to be the main indicator of biodegradable organic matter and bacterial oxygen consumption. However, the results were negative, showing a decreasing trend. This means that the oxygen content was lower in the majority of reservoirs, which is attributed to the decomposition of ammonia nitrogen and the presence of organic matter. These findings significantly contribute to the development of appropriate programs for efficient water quality monitoring and the development of reservoir-specific management strategies. This study suggests that there is a need for continuous monitoring of these parameters, together with the extension of the program to additional reservoirs and water quality indicators, along with the use of advanced modeling techniques to clarify the underlying factors that connect water quality parameters in these complex reservoir ecosystems. Full article
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<p>Sampling sites map of surface water of selected reservoirs. Satellite Imagery Source: Esri, ArcGIS Imagery.</p>
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<p>Correlation analysis of COD<sub>Mn</sub> and COD.</p>
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<p>Correlation analysis of COD<sub>Mn</sub> and COD.</p>
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<p>Correlation analysis of COD<sub>Mn</sub> and BOD<sub>5</sub>.</p>
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<p>Correlation analysis of COD<sub>Mn</sub> and BOD<sub>5</sub>.</p>
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<p>Correlation analysis of BOD<sub>5</sub> and COD.</p>
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<p>The relationship between the BOD<sub>5</sub> concentration change and index ratio among the five reservoirs.</p>
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<p>Result statistics chart of DO, COD, COD<sub>Mn</sub>, BOD<sub>5</sub>, and NH<sub>3</sub>-H among the five reservoirs.</p>
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<p>Result statistics chart of DO, COD, COD<sub>Mn</sub>, BOD<sub>5</sub>, and NH<sub>3</sub>-H among the five reservoirs.</p>
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<p>Result statistics chart of water temperature, transparency, chlorophyll-a, and turbidity in the five reservoirs.</p>
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<p>Result statistics chart of water temperature, transparency, chlorophyll-a, and turbidity in the five reservoirs.</p>
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<p>Result statistics chart of water temperature, transparency, chlorophyll-a, and turbidity in the five reservoirs.</p>
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26 pages, 19626 KiB  
Article
Hydrogeochemistry, Water Quality, and Health Risk Analysis of Phreatic Groundwater in the Urban Area of Yibin City, Southwestern China
by Xiangchuan Wu, Jinhai Yu, Shiming Yang, Yunhui Zhang, Qili Hu, Xiaojun Xu, Ying Wang, Yangshuang Wang, Huan Luo and Zhan Xie
Water 2024, 16(24), 3599; https://doi.org/10.3390/w16243599 (registering DOI) - 13 Dec 2024
Viewed by 377
Abstract
With rapid urbanization, intensified agricultural activities, and industrialization, groundwater resources are increasingly threatened by pollution. Industrial wastewater discharge and the extensive use of agricultural fertilizers in particular, have had substantial impacts on groundwater quality. This study examines 18 groundwater samples collected from the [...] Read more.
With rapid urbanization, intensified agricultural activities, and industrialization, groundwater resources are increasingly threatened by pollution. Industrial wastewater discharge and the extensive use of agricultural fertilizers in particular, have had substantial impacts on groundwater quality. This study examines 18 groundwater samples collected from the main urban area of Yibin City to assess hydrochemical characteristics, spatial distribution, source attribution, water quality, and human health risks. Statistical analysis reveals significant exceedances in TDS, NO3, Mn, and As levels in groundwater, with elevated concentrations of B as well. Isotopic analysis identifies atmospheric rainfall as the primary recharge source for groundwater in the area, with water–rock interactions and limestone dissolution playing key roles in shaping its chemical composition. Applying the Entropy-Weighted Water Quality Index (EWQI) for a comprehensive water quality assessment, the study found that 94.44% of groundwater samples were rated as “good”, indicating relatively high overall water quality. Deterministic health risk assessments indicate that 72.22% of the groundwater samples have non-carcinogenic health risks below the threshold of 1, while 66.67% have carcinogenic health risks below 1.00 × 10−4. Monte Carlo simulations produced similar results, reinforcing the reliability of the health risk assessment. Although the study area’s groundwater quality is generally good, a significant human health risk persists, underscoring the need to ensure the safety of drinking and household water for local residents. This study provides a valuable reference for the rational management and remediation of groundwater resources. Full article
(This article belongs to the Section Wastewater Treatment and Reuse)
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<p>(<b>a</b>) Location of Yibin in China. (<b>b</b>) Location of study area in Yibin. (<b>c</b>) Location of groundwater sampling sites and geological map in the study area (sample size = 18). <b>J<sub>2S</sub></b> refers to the Middle Jurassic strata, <b>J<sub>1</sub><sub>–2</sub>zl</b> refers to the Lower to Middle Jurassic strata, <b>J<sub>3</sub></b> represents the Upper Jurassic strata, <b>K<sub>1</sub></b> denotes the Lower Cretaceous strata, and <b>K<sub>2</sub></b> represents the Upper Cretaceous strata. <b>O</b> refers to the Ordovician strata, <b>P<sub>1</sub></b> indicates the Lower Permian strata, <b>S</b> corresponds to the Silurian strata, while <b>T<sub>1</sub></b>, <b>T<sub>2</sub></b>, and <b>T<sub>3</sub></b> represent the Lower, Middle, and Upper Triassic strata.</p>
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<p>The different types of land use in the study area and the distribution of the samples.</p>
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<p>The flowchart of the workflows in this study.</p>
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<p>Box plots of macronutrient ions and trace elements in groundwater in the main urban area of Yibin City. (<b>a</b>–<b>o</b>) represent the box plots of pH, TDS, Ca<sup>2+</sup>, Mg<sup>2+</sup>, Na<sup>+</sup>, F<sup>−</sup>, Cl<sup>−</sup>, SO₄²<sup>−</sup>, NO<sub>3</sub><sup>−</sup>, B, Mn, As, HCO<sub>3</sub><sup>−</sup>, temperature (T), and dissolved oxygen (DO), respectively.</p>
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<p>Spatial distribution map of major elements: (<b>a</b>) pH, (<b>b</b>) TDS, (<b>c</b>) Ca<sup>2+</sup>, (<b>d</b>) Mg<sup>2+</sup>, (<b>e</b>) Na<sup>+</sup>, (<b>f</b>) F<sup>−</sup>, (<b>g</b>) Cl<sup>−</sup>, (<b>h</b>) SO<sub>4</sub><sup>2−</sup>, (<b>i</b>) NO<sub>3</sub><sup>−</sup>, (<b>j</b>) B, (<b>k</b>) Mn, and (<b>l</b>) As (sample size = 18).</p>
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<p>(<b>a</b>) Groundwater Total Hardness Classification Chart. (<b>b</b>) Piper trilinear diagram of samples in the study area.</p>
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<p>Cation–Anion Molar Mixing Ratio Diagram for (<b>a</b>) Cations and (<b>b</b>) Anions; and Hydrogeochemical processes based on Gibbs diagrams for (<b>c</b>) anions and (<b>d</b>) cations.</p>
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<p>Scatter plots of (<b>a</b>) Cl<sup>−</sup> vs. Na<sup>+</sup> + K<sup>+</sup>; (<b>b</b>) (HCO<sub>3</sub><sup>−</sup> + SO<sub>4</sub><sup>2−</sup>) vs. (Ca<sup>2+</sup> + Mg<sup>2+</sup>); (<b>c</b>) HCO<sub>3</sub><sup>−</sup> vs. Ca<sup>2+</sup>; (<b>d</b>) HCO<sub>3</sub><sup>−</sup> vs. (Ca<sup>2+</sup> + Mg<sup>2+</sup>); (<b>e</b>) SO<sub>4</sub><sup>2−</sup> vs. Ca<sup>2+</sup>; (<b>f</b>) Ca<sup>2+</sup> vs. Mg<sup>2+</sup>; (<b>g</b>) Ca<sup>2+</sup> + Mg<sup>2+</sup>-(HCO<sub>3</sub><sup>−</sup> + SO<sub>4</sub><sup>2−</sup>) vs. Na<sup>+</sup> + K<sup>+</sup>−Cl<sup>−</sup>; (<b>h</b>) chloro alkaline indices CAI-Ι and CAI-П; (<b>i</b>) Saturation index of calcite, dolomite, gypsum, and halite.</p>
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<p>Scatterplot of stable isotopes of hydrogen and oxygen in groundwater samples from the main city of Yibin. GMWL refers to [<a href="#B58-water-16-03599" class="html-bibr">58</a>], LMWL refers to [<a href="#B59-water-16-03599" class="html-bibr">59</a>].</p>
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<p>Correlation diagram for (<b>a</b>) Sr vs. <sup>87</sup>Sr/<sup>86</sup>Sr; (<b>b</b>) Mg<sup>2+</sup>/Ca<sup>2+</sup> vs. <sup>87</sup>Sr/<sup>86</sup>Sr.</p>
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<p>Spatial distribution of groundwater quality for drinking purposes based on EWQI.</p>
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<p>Spatial distribution characteristics of HI and CR. (<b>a</b>) HI to children; (<b>b</b>) HI to adults; (<b>c</b>) CR to children; (<b>d</b>) CR to adults.</p>
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<p>Probabilistic assessment results based on the Monte Carlo simulation: (<b>a</b>) HI to children; (<b>b</b>) HI to adults; (<b>c</b>) CR to children; (<b>d</b>) CR to adults and the sensitivities of each parameter on the HHR model: (<b>e</b>) Sensitivities on HI; (<b>f</b>) Sensitivities on CR.</p>
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15 pages, 1087 KiB  
Article
A Probabilistic Model for Predicting the Performance of a Stormwater Overflow Structure as Part of a Stormwater Treatment Plant
by Jarosław Górski, Bartosz Szeląg, Łukasz Bąk and Anna Świercz
Water 2024, 16(24), 3598; https://doi.org/10.3390/w16243598 (registering DOI) - 13 Dec 2024
Viewed by 275
Abstract
The purpose of this study was to attempt to develop a stochastic model that describes the operation of the stormwater overflow located in the stormwater sewerage system. The model built for this study makes it possible to simulate the annual volume of the [...] Read more.
The purpose of this study was to attempt to develop a stochastic model that describes the operation of the stormwater overflow located in the stormwater sewerage system. The model built for this study makes it possible to simulate the annual volume of the stormwater discharge, the maximum volume of the overflow discharge in a precipitation event, and the share of the latter in the total amount of stormwater conveyed directly, without pre-treatment, to the receiver. The dependence obtained with the linear regression method was employed to identify the occurrence of stormwater discharge. The prediction of the synthetic annual rainfall series was made using the Monte Carlo method. This was performed based on the determined log-normal distribution, the parameters of which were specified using 13-year rainfall series. Additionally, simulation of the stormwater overflow operation was performed with the use of a calibrated hydrodynamic model of the catchment. The model was developed using the Storm Water Management Model (SWMM). The results of the hydrodynamic simulations of the volume and number of discharges were within the scope of the probabilistic solution, which confirms the applicative character of the method presented in this study, intended to assess the operation of stormwater overflow. Full article
(This article belongs to the Special Issue Urban Stormwater Control, Utilization, and Treatment)
13 pages, 3151 KiB  
Article
Analysis of the Relationship Between Groundwater Dynamics and Changes in Water and Salt in Soil Under Subsurface Pipe Salt Drainage Technology
by Xu Wang, Jingli Shen, Liqin Fan and Jinjun Cai
Water 2024, 16(24), 3597; https://doi.org/10.3390/w16243597 (registering DOI) - 13 Dec 2024
Viewed by 310
Abstract
Groundwater conditions are crucial for understanding the evolution of soil salinization. The installation of subsurface pipes significantly alters both the distribution of water and salt in the soil and the groundwater depth; these dynamics and their interrelationships warrant further investigation. To clarify the [...] Read more.
Groundwater conditions are crucial for understanding the evolution of soil salinization. The installation of subsurface pipes significantly alters both the distribution of water and salt in the soil and the groundwater depth; these dynamics and their interrelationships warrant further investigation. To clarify the relationship between groundwater dynamics and changes in water and salt in soil under subsurface pipe salt drainage conditions in the Yinchuan region of Ningxia, groundwater observation wells and soil sample monitoring points were established in Pingluo County. A combined approach of in situ monitoring and laboratory testing was employed to analyze changes in groundwater depth and salinity and their effects on water and salt in soil. The findings revealed that changes in groundwater depth and salinity exhibited clear seasonal patterns. The groundwater depth was deepest at 1.97 m in October and shallowest at 1.62 m in July. The salinity was highest at 22.28 g/L in April and lowest at 18.24 g/L in August. In summer, the groundwater was shallower and had lower salinity, while in other seasons, it was deeper with higher salinity. Soil salinity was lowest in July at 4.58 g/kg and highest in April at over 5.5 g/kg. It decreased with increasing groundwater depth, demonstrating a linear relationship. Additionally, soil salinity and groundwater salinity exhibited synchronous fluctuations, exhibiting an exponential relationship. Based on these observations, a model was developed to describe the relationship among groundwater salinity, groundwater depth, and soil salinity under subsurface pipe salt drainage conditions in the Yinbei region of Ningxia. This model was validated against measured data, yielding a correlation coefficient R2 of 0.7238. These findings provide a reference for analyzing the relationship between soil salinity and groundwater in similar regions. Full article
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<p>Geographical position of experimental area (The colors red, yellow, and green represent the mountains, hills, and plains in Ningxia, respectively).</p>
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<p>Monitoring site of the experimental area (the dashed blue line indicates the subsurface pipe, and the black dots indicate the monitoring points, the red line square is the experimental area).</p>
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<p>Variations in groundwater depth.</p>
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<p>Variations in groundwater salinity.</p>
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<p>Relationship between soil moisture and groundwater depth.</p>
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<p>Relationship between soil moisture and groundwater salinity.</p>
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<p>Variations in soil salinity and groundwater depth.</p>
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<p>The fitted relationships between soil salinity and groundwater depth. (<b>A</b>) Linear relationship fitting. (<b>B</b>) Exponential relationship fitting.</p>
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<p>The fitted relationships between soil salinity and groundwater depth. (<b>A</b>) Linear relationship fitting. (<b>B</b>) Exponential relationship fitting.</p>
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<p>Variations in soil salinity and groundwater salinity.</p>
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<p>The fitted relationships between soil salinity and groundwater salinity. (<b>A</b>) Linear relationship fitting. (<b>B</b>) Exponential relationship fitting.</p>
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<p>Relationship between <span class="html-italic">N</span> and groundwater depth.</p>
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21 pages, 11003 KiB  
Article
A Numerical Study on Impact of Coal Mining Activity and Mine Water Drainage on Flow and Transport Behavior in Groundwater
by Kaisar Ahmat, Hao Lu and Huiquan Liu
Water 2024, 16(24), 3596; https://doi.org/10.3390/w16243596 (registering DOI) - 13 Dec 2024
Viewed by 431
Abstract
Under the dual carbon mission, more and more coal mines will face shutting down in the future and stop treating mine water drainage, which, if it escapes, may cause severe secondary damage to the local groundwater quality. Wudong Coal Mine is a currently [...] Read more.
Under the dual carbon mission, more and more coal mines will face shutting down in the future and stop treating mine water drainage, which, if it escapes, may cause severe secondary damage to the local groundwater quality. Wudong Coal Mine is a currently active subsurface coal mine in Xinjiang, China, that shows high-salinity characteristics. To forecast and discuss future possible groundwater quality damages and potential solutions, we here introduce a model prediction study on the effects of water pollution by coal mine drainage. The study protocol first involves creating a calibrated 2D groundwater flow model by use of FEFLOW software, then designing several flow and solute transport prediction analyses under changing mine water drainage conditions, different pollution source areas and water treatment pumping wells to discuss future prominent flow and transport behavior, as well as water treatment-affecting factors. It has been shown that mine water drainage plays a critical role in maintaining the mine water solute distribution, as without mine draining, local flow and solute distribution change dramatically, altering the groundwater capture zone, and may change the plume-migrating direction from upstream to downstream. A larger pollution source could produce a higher concentration of pollutants and a larger pollution-coverage area. To reduce pollutant concentrations, mine water treatment pumping wells with higher pumping rates can be applied as a useful remedial measure to effectively prevent the pollutant plume front from reaching the important drinking and irrigation water source of the region, Urumqi River. The results of this study can give important suggestions and decision-making support for authorities focused on water treatment and environmental protection decision-making in the region. Full article
(This article belongs to the Section Hydrogeology)
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<p>Study area’s geological location.</p>
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<p>Model boundary condition.</p>
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<p>Model mesh design.</p>
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<p>Initial flow distribution (<b>a</b>) and model flow chart (<b>b</b>).</p>
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<p>Initial calibrated head distribution (<b>a</b>) and hydrogeological parameter zoning map (<b>b</b>).</p>
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<p>Model validation by measured and modeled hydraulic head.</p>
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<p>Flow distribution change at different times.</p>
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<p>Solute distribution at different times without stopping drainage.</p>
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<p>Solute distribution at different times without stopping drainage.</p>
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<p>Base case flow distribution change after stopping mine water drainage.</p>
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<p>Base case solute distribution change with stopping mine water draining in the 5th year.</p>
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<p>Larger pollution source with flow distribution change (<b>a</b>) and solute distribution with stopping drainage (<b>b</b>−<b>d</b>).</p>
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<p>Observation point pollutant concentration history under different pollution source.</p>
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<p>A treatment rate of 200 m<sup>3</sup>/d of well pumping caused a flow distribution change (<b>a</b>) and solute distribution when stopping mine water drainage (<b>b</b>–<b>d</b>).</p>
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<p>Impact of treatment rate of 1000 m<sup>3</sup>/d of well pumping, which caused flow distribution change (<b>a</b>) and solute distribution when stopping mine water drainage (<b>b</b>–<b>d</b>).</p>
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<p>Observation point pollutant concentration history at different pumping rates.</p>
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23 pages, 968 KiB  
Article
Exploring Aquaculture Professionals’ Perceptions of Artificial Intelligence: Quantitative Insights into Mediterranean Fish Health Management
by Dimitris C. Gkikas, Vasileios P. Georgopoulos and John A. Theodorou
Water 2024, 16(24), 3595; https://doi.org/10.3390/w16243595 (registering DOI) - 13 Dec 2024
Viewed by 271
Abstract
This study aims to explore aquaculture professionals’ perspectives on, attitudes towards and understanding of Mediterranean farm fish health management, regarding Artificial Intelligence (A.I.), and to shed light on the factors that affect its adoption. A survey was distributed during a major fish health [...] Read more.
This study aims to explore aquaculture professionals’ perspectives on, attitudes towards and understanding of Mediterranean farm fish health management, regarding Artificial Intelligence (A.I.), and to shed light on the factors that affect its adoption. A survey was distributed during a major fish health management conference, representing more than 70% of Greek domestic production. A total of 73 questionnaires were collected, for which descriptive statistics and statistical analysis followed. Gender and age were shown to affect interest in A.I. and in viewing A.I. as a partner rather than a competitor. Age was additionally shown to affect trust in A.I. estimates and anticipation that A.I. will contribute to professional development. Education level shows no significant effect. Knowledge of A.I. is positively correlated with A.I. usage (r = 0.43, p < 0.05), as is interest in learning about A.I. (r = 0.64). A.I. usage is in turn positively correlated with eagerness to see its contribution (r = 0.72). Despite the fact that 64.4% characterized their knowledge as little or non-existent, 67.1% expressed interest in learning more, while 43.8% believe that A.I. will revolutionize aquaculture and 74% do not fear they will be replaced by A.I. in the future. The findings highlight the importance of targeted educational initiatives to bridge the knowledge gap and encourage trust in A.I. technologies. Full article
(This article belongs to the Special Issue Sustainable Transformation of Aquaculture in Marine Environments)
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<p>Demographics.</p>
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<p>Preferred source of information.</p>
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<p>Emotional response.</p>
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<p>Correlations heatmap graph.</p>
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19 pages, 18178 KiB  
Article
Spatiotemporal Variations of Precipitation Extremes and Population Exposure in the Beijing–Tianjin–Hebei Region, China
by Hao Lin, Xi Yu, Yumei Lin and Yandong Tang
Water 2024, 16(24), 3594; https://doi.org/10.3390/w16243594 - 13 Dec 2024
Viewed by 345
Abstract
In recent years, precipitation extremes in China have increased due to global warming, posing a significant threat to human life and property. It is thus crucial to understand the changes in population exposure to precipitation extremes and the causes of these changes, since [...] Read more.
In recent years, precipitation extremes in China have increased due to global warming, posing a significant threat to human life and property. It is thus crucial to understand the changes in population exposure to precipitation extremes and the causes of these changes, since complex terrain areas are not accurately simulated by rain gauge interpolation data. Thus, we first used three satellite-based precipitation products—TRMM 3B42, CHIRPS, and CMORPH—combined with population data to analyze the spatiotemporal changes of precipitation extremes and population exposure from 1998 to 2019 in the Beijing–Tianjin–Hebei (BTH) region. In addition, the contributions of population, climate, and composite factors were quantified. The results showed that TRMM 3B42 outperformed the other two datasets in the BTH region. Over the past 22 years, the precipitation extremes in the central and northeastern regions, especially in Beijing, reached 2.5 days per decade, while the northern and southern regions showed a downward trend. The highest population exposure was mainly concentrated in central Beijing, most areas of Tianjin, and the urban centers of cities in southeastern Hebei province. Compared to the 2000s, a significant increase in exposure was observed in Beijing, Tianjin, and Zhangjiakou in the 2010s, whereas other regions showed negligible changes during this period. Climatic factors had the greatest influence on population exposure in most cities such as Qinhuangdao and Hengshui, where their climatic contribution exceeded 70%. While population change was more responsible for the increase in population exposure in the densely populated cities such as Tianjin, Handan, and Langfang, these cities contributed over 60% of the population. The interaction effect in Beijing and Tianjin was relatively obvious. The results of this study can provide a scientific basis for formulating targeted disaster risk management measures against climate change in the BTH region. Full article
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<p>The location of our study area.</p>
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<p>The locations of the rain gauge stations.</p>
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<p>Scatter plots of annual precipitation between precipitation products including and corresponding rain gauge data from 1998–2019: (<b>a</b>) TRMM 3B42, (<b>b</b>) CHIRPS, (<b>c</b>) CMORPH.</p>
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<p>Scatter plots of annual precipitation between precipitation products including and corresponding rain gauge data from 1998–2019: (<b>a</b>) TRMM 3B42, (<b>b</b>) CHIRPS, (<b>c</b>) CMORPH.</p>
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<p>Scatter plots of season precipitation between precipitation products including and corresponding rain gauge data from 1998–2019: (<b>a</b>) TRMM 3B42, (<b>b</b>) CHIRPS, (<b>c</b>) CMORPH.</p>
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<p>Scatter plots of precipitation extreme events between precipitation products including and corresponding rain gauge data from 1998–2019: (<b>a</b>) TRMM 3B42, (<b>b</b>) CHIRPS, (<b>c</b>) CMORPH.</p>
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<p>Scatter plots of precipitation extreme events between precipitation products including and corresponding rain gauge data from 1998–2019: (<b>a</b>) TRMM 3B42, (<b>b</b>) CHIRPS, (<b>c</b>) CMORPH.</p>
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<p>Spatial distribution of days of precipitation extremes.</p>
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<p>Sen’s Slope of R95D (1998–2019).</p>
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<p>Mann–Kendall Z-Value of R95D (1998–2019).</p>
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<p>Population exposure in Hebei Province from 1998 to 2019.</p>
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<p>Changes in population exposure to precipitation extremes in the BTH region in the 2010s compared with the 2000s.</p>
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<p>Changes in population in the BTH region in the 2010s compared with the 2000s.</p>
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<p>Effects of the changes of (<b>a</b>) climate, (<b>b</b>) population, and (<b>c</b>) their interaction on the exposure in BTH region.</p>
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<p>Effects of changes in population, climate, and their interaction on the exposure of different cities.</p>
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8 pages, 199 KiB  
Editorial
Application of Biomass Functional Materials in the Environment
by Yiting Luo and Rongkui Su
Water 2024, 16(24), 3593; https://doi.org/10.3390/w16243593 - 13 Dec 2024
Viewed by 697
Abstract
With the intensification of global environmental issues, traditional materials science is facing unprecedented challenges [...] Full article
15 pages, 3606 KiB  
Article
Global Water Use and Its Changing Patterns: Insights from OECD Countries
by Xiaomei Zhu, Minglei Hou and Jiahua Wei
Water 2024, 16(24), 3592; https://doi.org/10.3390/w16243592 - 13 Dec 2024
Viewed by 325
Abstract
Water resources are an important foundation for sustainable socioeconomic development. Revealing water use efficiency, the change in water use trends, and their driving mechanisms is essential for facilitating the scientific and reasonable prediction of water demand, thereby guiding the scientific planning and management [...] Read more.
Water resources are an important foundation for sustainable socioeconomic development. Revealing water use efficiency, the change in water use trends, and their driving mechanisms is essential for facilitating the scientific and reasonable prediction of water demand, thereby guiding the scientific planning and management of water resources. This study utilizes socioeconomic and water usage data from 65 countries spanning the years 1970 to 2020, employing the panel smooth transfer regression (PSTR) model to analyze the relationship between per capita total water withdrawal and per capita GDP. Additionally, Random Forest (RF) methods and empirical statistical analyses are implemented to identify the driving factors, control variables, and critical thresholds of water use trends in countries with different levels of development. The results show that: (1) there exists a nonlinear relationship between per capita total water withdrawal and per capita GDP on a global scale, with 70% of the countries exhibiting an inverted U-type trend in water usage; (2) the observed decline in per capita total water withdrawal in relation to per capita GDP is primarily driven by technological advancements and the optimization and enhancement of production structure; (3) common characteristics of OECD (Organization for Economic Cooperation and Development) countries that have reached their peak water usage include a service sector contribution to GDP exceeding 60%, urbanization levels at 70%, and per capita GDP surpassing USD 20,000. The observed changes in water use trends and the characteristic indicators associated with peak water usage, under conditions devoid of engineering interventions and resources constraints, can serve as valuable references for medium- and long-term water resources planning and water demand management in developing nations. Full article
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<p>Methodology flowchart for the changing patterns and drivers of global water use.</p>
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<p>Fitting curves of per capita total water withdrawal and per capita GDP for the years 1995 and 2020: (<b>a</b>) global; (<b>b</b>) OECD.</p>
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<p>Trends in total water withdrawals and per capita total water withdrawal with changes in per capita GDP: (<b>a</b>) inverted U-type, (<b>b</b>) rising type, and (<b>c</b>) wave type.</p>
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<p>Spatial distributions of total water withdrawals and per capita total water withdrawal, categorized by water use trends in relation to per capita GDP.</p>
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<p>Importance of characteristic variables for the change in per capita total water withdrawal with decreasing per capita GDP: (<b>a</b>) global; (<b>b</b>) OECD and non-OECD.</p>
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<p>Characteristics of peak times and corresponding socioeconomic variables for various countries: (<b>a</b>) OECD; (<b>b</b>) non-OECD.</p>
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