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Search Results (13,016)

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Keywords = meteorology

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13 pages, 4992 KiB  
Article
Prediction of the Future Evolution Trends of Prunus sibirica in China Based on the Key Climate Factors Using MaxEnt Modeling
by Jiazhi Wang, Jiming Cheng, Chao Zhang, Yingqun Feng, Lang Jin, Shuhua Wei, Hui Yang, Ziyu Cao, Jiuhui Peng and Yonghong Luo
Biology 2024, 13(12), 973; https://doi.org/10.3390/biology13120973 - 25 Nov 2024
Abstract
Mountain apricot (Prunus sibirica) is an important fruit tree variety, and has a wide range of planting and application value in China and even the world. However, the current research on the suitable distribution area of P. sibirica is still inconclusive. [...] Read more.
Mountain apricot (Prunus sibirica) is an important fruit tree variety, and has a wide range of planting and application value in China and even the world. However, the current research on the suitable distribution area of P. sibirica is still inconclusive. In this study, we retrieved distribution data for P. sibirica in China from the Global Biodiversity Information Facility (GBIF), and identified six key environmental factors influencing its distribution through cluster analysis. Using these six selected climate factors and P. sibirica distribution points in China, we applied the maximum entropy model (MaxEnt) to evaluate 1160 candidate models for parameter optimization. The final results predict the potential distribution of P. sibirica under the current climate as well as two future climate scenarios (SSPs126 and SSPs585). This study shows that the model optimized with six key climate factors (AUC = 0.897, TSS = 0.658) outperforms the full model using nineteen climate factors (AUC = 0.894, TSS = 0.592). Under the high-emission scenario (SSPs585), the highly suitable habitat for P. sibirica is expected to gradually shrink towards the southeast and northwest, while expanding in the northeast and southwest. After the 2050s, highly suitable habitats are projected to completely disappear in Shandong, while new suitable areas may emerge in Tibet. Additionally, the total area of suitable habitat is projected to increase in the future, with a more significant expansion under the high-emission scenario (SSPs585) compared to the low-emission scenario (SSPs126) (7.33% vs. 0.16%). Seasonal changes in precipitation are identified as the most influential factor in driving the distribution of P. sibirica. Full article
(This article belongs to the Section Plant Science)
18 pages, 3244 KiB  
Article
Characteristics of Meteorological Drought Evolution in the Yangtze River Basin
by Wenchuan Bai, Cicheng Zhang, Xiong Xiao, Ziying Zou, Zelin Liu, Peng Li, Jiayi Tang, Tong Li, Xiaolu Zhou and Changhui Peng
Water 2024, 16(23), 3391; https://doi.org/10.3390/w16233391 - 25 Nov 2024
Abstract
Amid global climate change, recurrent drought events pose significant challenges to regional water resource management and the sustainability of socio-economic growth. Thus, understanding drought characteristics and regional development patterns is essential for effective drought monitoring, prediction, and the creation of robust adaptation strategies. [...] Read more.
Amid global climate change, recurrent drought events pose significant challenges to regional water resource management and the sustainability of socio-economic growth. Thus, understanding drought characteristics and regional development patterns is essential for effective drought monitoring, prediction, and the creation of robust adaptation strategies. Most prior research has analyzed drought events independently in spatial and temporal dimensions, often overlooking their dynamic nature. In this study, we employ a three-dimensional methodology that accounts for spatiotemporal continuity to identify and extract meteorological drought events based on a 3-month standardized precipitation evapotranspiration index (SPEI3). Measured by the SPEI3 index, the incidence of drought increased in the middle part of the basin, especially in some parts of Sichuan and Yunnan province, and the frequency of drought events decreased in the upper reaches. We evaluate drought events within the Yangtze River basin from 1980 to 2016 by examining five variables: chronology, extent, severity, duration, and epicenter locations. The results show that a total of 97 persisting drought events lasting at least 3 months have been identified in Yangtze River basin. Most events have a duration between 4 and 7 months. The findings indicate that while the number of drought events in the Yangtze River basin has remained unchanged, the intensity, duration, and severity of these events have shown a slight increase from 1980 to 2016. The drought events gradually moved from the western and southeastern parts of the basin to the central region. The most severe drought event occurred between January 2011 and October 2011, with a duration of 10 months and an affected area of 0.94 million km2, impacting over fifty percent of the basin. Changes in wetness and dryness in the Yangtze River basin are closely related to El Niño/Southern Oscillation (ENSO) events, with a positive correlation between the intensity of cold events and the probability of extreme drought. This study enhances our understanding of the dynamics and evolution of drought events in the Yangtze River basin, providing crucial insights for better managing water resources and developing effective adaptation strategies. Full article
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<p>Schematic representation of the continuity of drought area in time.</p>
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<p>(<b>a</b>) Time variation. (<b>b</b>) Spatial variation in SPEI3 in the Yangtze River Basin, 1980–2016.</p>
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<p>Frequency and probability distribution of the following drought characteristic variables: (<b>a</b>) duration, (<b>b</b>) intensity, (<b>c</b>) severity, and (<b>d</b>) area. The horizontal axis represents these variables, with each interval width appropriately divided based on the data range and distribution characteristics. The vertical axis indicates the frequency of each variable interval.</p>
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<p>Statistics summary of the following identified three-dimensional SPEI3 drought events: (<b>a</b>) drought number, (<b>b</b>) drought severity, (<b>c</b>) drought intensity, and (<b>d</b>) drought area. The linear trend line is represented by the blue line.</p>
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<p>Spatial distribution of the centroid of drought events in the Yangtze River Basin are as follows: (<b>a</b>) 1980–1989, (<b>b</b>) 1990–1999, (<b>c</b>) 2000–2009, and (<b>d</b>) 2010–2016. Events lasting for at least 3 months are shown.</p>
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<p>Relationship between drought-affected area (A), severity (S), and intensity (I) with duration (D).</p>
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<p>Typical drought progression from January 2011 to November 2011, with the dynamic evolution process of the critical period as follows (<b>a</b>): from a three-dimensional perspective, and (<b>b</b>): from the latitude–longitude plane. The bottom layer of <a href="#water-16-03391-f007" class="html-fig">Figure 7</a>a shows the spatial distribution of cumulated SPEI3 during the drought event. The arrows indicate the migration trajectory of the drought centroid in <a href="#water-16-03391-f007" class="html-fig">Figure 7</a>b.</p>
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20 pages, 3104 KiB  
Article
Sensitivity of Streamflow to Changing Rainfall and Evapotranspiration in Catchments Across the Nile Basin
by Charles Onyutha, Brian Odhiambo Ayugi, Kenny Thiam Choy Lim Kam Sian, Hassen Babaousmail, Wenseslas Arineitwe, Josephine Taata Akobo, Cyrus Chelangat and Ambrose Mubialiwo
Atmosphere 2024, 15(12), 1415; https://doi.org/10.3390/atmos15121415 - 25 Nov 2024
Abstract
This research focuses on the complex dynamics governing the sensitivity of streamflow to variations in rainfall and potential evapotranspiration (PET) within the Nile basin. By employing a hydrological model, our study examines the interrelationships between meteorological variables and hydrological responses across six catchments [...] Read more.
This research focuses on the complex dynamics governing the sensitivity of streamflow to variations in rainfall and potential evapotranspiration (PET) within the Nile basin. By employing a hydrological model, our study examines the interrelationships between meteorological variables and hydrological responses across six catchments (Blue Nile, El Diem, Kabalega, Malaba, Mpanga, and Ribb) and explores the intricate balance between rainfall, PET, and streamflow. Nash Sutcliffe Efficiency (NSE) for calibration of the hydrological model ranged from 0.636 (Ribb) to 0.831 (El Diem). For validation, NSE ranged from 0.608 (Ribb) to 0.811 (Blue Nile). With rainfall kept constant while PET was increased by 5%, the streamflows of the Blue Nile, El Diem, Kabalega, Malaba, Mpanga, and Ribb decreased by 7.00, 5.08, 2.49, 4.10, 1.84, and 7.67%, respectively. With the original PET data unchanged, increasing rainfall of the Blue Nile, El Diem, Kabalega, Malaba, Mpanga, and Ribb by 5% led to an increase in streamflow by 9.02, 9.87, 5.38, 4.34, 6.58, and 8.32%, respectively. The research reveals that the rate at which a catchment losing water to the atmosphere (determined by PET) substantially influences its drying rate. Utilizing linear models, we demonstrate that the surplus rainfall available for increasing streamflow (represented by model intercepts) amplifies with higher rainfall intensities. This highlights the pivotal role of rainfall in shaping catchment water balance dynamics. Moreover, our study stresses the varied sensitivities of catchments within the basin to changes in PET and rainfall. Catchments with lower PET exhibit heightened responsiveness to increasing rainfall, accentuating the influence of evaporative demand on streamflow patterns. Conversely, regions with higher PET rates necessitate refined management strategies due to their increased sensitivity to changes in evaporative demand. Understanding the intricate interplay between rainfall, PET, and streamflow is paramount for developing adaptive strategies amidst climate variability. By examining these relationships, our research contributes essential knowledge for sustainable water resource management practices at both the catchment and regional scales, especially in regions susceptible to varying sensitivities of catchments to climatic conditions. Full article
(This article belongs to the Section Biosphere/Hydrosphere/Land–Atmosphere Interactions)
26 pages, 7934 KiB  
Article
Study of Land Surface Changes in Highland Environments for the Sustainable Management of the Mountainous Region in Gilgit-Baltistan, Pakistan
by Amjad Ali Khan, Xian Xue, Hassam Hussain, Kiramat Hussain, Ali Muhammad, Muhammad Ahsan Mukhtar and Asim Qayyum Butt
Sustainability 2024, 16(23), 10311; https://doi.org/10.3390/su162310311 - 25 Nov 2024
Abstract
Highland ecologies are the most susceptible to climate change, often experiencing intensified impacts. Due to climate change and human activities, there were dramatic changes in the alpine domain of the China–Pakistan Economic Corridor (CPEC), which is a vital project of the Belt and [...] Read more.
Highland ecologies are the most susceptible to climate change, often experiencing intensified impacts. Due to climate change and human activities, there were dramatic changes in the alpine domain of the China–Pakistan Economic Corridor (CPEC), which is a vital project of the Belt and Road Initiative (BRI). The CPEC is subjected to rapid infrastructure expansion, which may lead to potential land surface susceptibility. Hence, focusing on sustainable development goals, mainly SDG 9 (industry, innovation, and infrastructure) and SDG 13 (climate action), to evaluate the conservation and management practices for the sustainable and regenerative development of the mountainous region, this study aims to assess change detection and find climatic conditions using multispectral indices along the mountainous area of Gilgit and Hunza-Nagar, Pakistan. It has yielded practical and highly relevant implications. For sustainable and regenerative ecologies, this study utilized 30 × 30 m Landsat 5 (TM), Landsat 7 (ETM+), and Landsat-8/9 (OLI and TIRS), and meteorological data were employed to calculate the aridity index (AI). The results of the AI showed a non-significant decreasing trend (−0.0021/year, p > 0.05) in Gilgit and a significant decreasing trend (−0.0262/year, p < 0.05) in Hunza-Nagar. NDVI distribution shows a decreasing trend (−0.00469/year, p > 0.05), while NDWI has depicted a dynamic trend in water bodies. Similarly, NDBI demonstrated an increasing trend, with rates of 79.89%, 87.69%, and 83.85% from 2008 to 2023. The decreasing values of AI mean a drying trend and increasing drought risk, as the study area already has an arid and semi-arid climate. The combination of multispectral indices and the AI provides a comprehensive insight into how various factors affect the mountainous landscape and climatic conditions in the study area. This study has practical and highly relevant implications for policymakers and researchers interested in research related to land use and land cover change, environmental and infrastructure development in alpine regions. Full article
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<p>Study area map: (<b>a</b>) Pakistan’s map; (<b>b</b>) map of the Gilgit-Baltistan (GB) Province of Pakistan; (<b>c</b>) study area location, with a 10 km buffer along the CPEC route in three districts (Gilgit, Hunza, and Nagar) of Gilgit-Baltistan, Pakistan.</p>
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<p>Distribution of minimum, mean, and maximum NDVIs from 2008 to 2023.</p>
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<p>Spatial pattern of NDVI change due to build-up in the study area from 2008 to 2023.</p>
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<p>Spatial pattern of NDVI change due to build-up in the study area from 2008 to 2023.</p>
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<p>Spatial pattern of NDVI change due to water in the study area from 2008 to 2023.</p>
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<p>Spatial pattern of NDVI change due to water in the study area from 2008 to 2023.</p>
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<p>Distribution of NDWI from 2008 to 2023, with four-year intervals.</p>
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<p>Spatial change in NDWI from 2008 to 2023 and significant at 0.01, 0.05 level.</p>
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<p>Spatial change in NDBI from 2008 to 2023 and significant at 0.01, 0.05 level.</p>
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<p>Distribution of NDBI from 2008 to 2023, with four-year intervals.</p>
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<p>The trend of the aridity index in the study area.</p>
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<p>Shows (<b>a</b>) population dynamics and (<b>b</b>) tourist flow in the study area.</p>
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<p>Temporal variation and linear trend along the CPEC route from 2008 to 2023; annual precipitation in (<b>a</b>) Gilgit and (<b>b</b>) Hunza-Nagar; annual temperature in (<b>c</b>) Gilgit and (<b>d</b>) Hunza-Nagar.</p>
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<p>Temporal variation and linear trend along the CPEC route from 2008 to 2023; annual precipitation in (<b>a</b>) Gilgit and (<b>b</b>) Hunza-Nagar; annual temperature in (<b>c</b>) Gilgit and (<b>d</b>) Hunza-Nagar.</p>
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26 pages, 8766 KiB  
Article
A Framework for Separating Climate and Anthropogenic Contributions to Evapotranspiration Changes in Natural to Agricultural Regions of Watersheds Based on Machine Learning
by Zixin Liang, Fengping Li, Hongyan Li, Guangxin Zhang and Peng Qi
Remote Sens. 2024, 16(23), 4408; https://doi.org/10.3390/rs16234408 - 25 Nov 2024
Abstract
Evapotranspiration is a crucial component of the water cycle and is significantly influenced by climate change and human activities. Agricultural expansion, as a major aspect of human activity, together with climate change, profoundly affects regional ET variations. This study proposes a quantification framework [...] Read more.
Evapotranspiration is a crucial component of the water cycle and is significantly influenced by climate change and human activities. Agricultural expansion, as a major aspect of human activity, together with climate change, profoundly affects regional ET variations. This study proposes a quantification framework to assess the impacts of climate change (ETm) and agricultural development (ETh) on regional ET variations based on the Random Forest algorithm. The framework was applied in a large-scale agricultural expansion area in China, specifically, the Songhua River Basin. Meteorological, topographic, and ET remote sensing data for the years of 1980 and 2015 were selected. The Random Forest model effectively simulates ET in the natural areas (i.e., forest, grassland, marshland, and saline-alkali land) in the Songhua River Basin, with R2 values of around 0.99. The quantification results showed that climate change has altered ET by −8.9 to 24.9 mm and −3.4 to 29.7 mm, respectively, in the natural areas converted to irrigated and rainfed agricultural areas. Deducting the impact of climate change on the ET variation, the development of irrigated and rainfed agriculture resulted in increases of 2.9 mm to 55.9 mm and 0.9 mm to 53.4 mm in ET, respectively, compared to natural vegetation types. Finally, the Self-Organizing Map method was employed to explore the spatial heterogeneity of ETh and ETm. In the natural–agriculture areas, ETm is primarily influenced by moisture conditions. When moisture levels are adequate, energy conditions become the predominant factor. ETh is intricately linked not only to meteorological conditions but also to the types of original vegetation. This study provides theoretical support for quantifying the effects of climate change and farmland development on ET, and the findings have important implications for water resource management, productivity enhancement, and environmental protection as climate change and agricultural expansion persist. Full article
21 pages, 5239 KiB  
Article
Influence of Tropical Cyclones and Cold Waves on the Eastern Guangdong Coastal Hydrodynamics: Processes and Mechanisms
by Yichong Zhong, Fusheng Luo, Yunhai Li, Yunpeng Lin, Jia He, Yuting Lin, Fangfang Shu and Binxin Zheng
J. Mar. Sci. Eng. 2024, 12(12), 2148; https://doi.org/10.3390/jmse12122148 - 25 Nov 2024
Abstract
In response to the intensification of global warming, extreme weather events, such as tropical cyclones (TCs) and cold waves (CWs) have become increasingly frequent near the eastern Guangdong coast, significantly affecting the structure and material transport of coastal waters. Based on nearshore-measured and [...] Read more.
In response to the intensification of global warming, extreme weather events, such as tropical cyclones (TCs) and cold waves (CWs) have become increasingly frequent near the eastern Guangdong coast, significantly affecting the structure and material transport of coastal waters. Based on nearshore-measured and remote sensing reanalysis data in the winter of 2011 and summer of 2012 on the eastern Guangdong coast, this study analyzed the nearshore hydrodynamic evolution process, influencing mechanism, and marine environmental effects under the influence of TCs and CWs, and further compared the similarities and differences between the two events. The results revealed significant seasonal variations in the hydrological and meteorological elements of the coastal waters, which were disrupted by the passage of TCs and CWs. The primary influencing factors were TC track and CW intensity. The current structure changed significantly during the TCs and CWs, with the TC destroying the original upwelling current and the CW affecting the prevailing northeastward current. Wind is one of the major forces driving nearshore hydrodynamic processes. According to the synchronous analysis of research data, the TC-induced water level rise is primarily attributed to the combined effects of wind stress curl and the Ekman effect, whereas the water level rise associated with CW is primarily linked to the Ekman effect. The water transport patterns during the TC and CW differed, with transport concentrated on the right side of the TC track and within the coastal strong-wind zones, respectively. Additionally, the temporal frequency domain of wavelet analysis highlighted the distinct nature of TC and CW signals, with 1–3 d and 4–8 d, respectively, and with TC signals being short-lived and rapid compared to the more sustained CW signals. This study enhances our understanding of the response of coastal hydrodynamics to extreme weather events on the eastern Guangdong coast, and the results can provide references for disaster management and protection of nearshore ocean engineering under extreme events. Full article
(This article belongs to the Section Physical Oceanography)
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<p>(<b>a</b>) Topographic map of the NSCS (GCC signifies the Guangdong Coastal Current; SCSWC signifies the Warm Current of the South China Sea; SCS, TWS, and NW Pacific signify the South China Sea, Taiwan Strait, and Northwest Pacific Ocean, respectively; the red box signifies the study area; blue, green, and yellow dots signify the tracks of TCs Talim and Doksuri, and the color and size of the dots signify the maximum wind speed and minimum central pressure of TCs, respectively; the blue arrows signify the direction of the CW). (<b>b</b>) Topographic map of the study area (red dots signify the location of each seabed-based observation station (W1 and W2)); the magenta inverted triangle signifies the location of the land meteorological observation station (F1); and the abscissa and ordinate axes of the coordinate system of station W1, W2, and F1 are along the shore (u’) and perpendicular to the shore (v’), respectively). Water depth data were obtained from the ETOPO Global Relief Model (public access). ETOPO Global Relief Model | National Centers for Environmental Information (NCEI) (noaa.gov), access on 20 June 2023).</p>
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<p>(<b>a</b>–<b>i</b>) The sea surface wind field (SSWF), sea surface current field (SSCF), and sea surface height anomaly (SSHA) distribution in the NSCS during the TC from 17 June to 3 July 2012 (black, red, and magenta arrows represent wind, current, and measured current vectors, respectively, and background color represents SSHA; (<b>a</b>–<b>c</b>) and (<b>f</b>–<b>h</b>) are the periods before, during, and after T1 and T2, respectively). SSWF, SSCF, and SSHA data were obtained from NCEP Climate Forecast System Version 2 Product (public access).</p>
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<p>(<b>a</b>–<b>i</b>) The sea surface wind field (SSWF), sea surface current field (SSCF), and sea surface height anomaly (SSHA) distribution in the NSCS during the CW from 5 November to 27 December 2011 (black, red, and magenta arrows represent wind, current vectors, and measured current vectors, respectively, and background color represents SSHA; (<b>a</b>–<b>c</b>), (<b>d</b>–<b>f</b>), and (<b>g</b>–<b>i</b>) are the periods before, during, and after C1, C2, and C3, respectively). SSWF, SSCF, and SSHA data were obtained from NCEP Climate Forecast System Version 2 Product (public access).</p>
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<p>Curves of summer and winter wind vector, air temperature, and air pressure at F1 station. (<b>a</b>) Summer wind vector. (<b>b</b>) Summer air temperature and air pressure. (<b>c</b>) Winter wind vector. (<b>d</b>) Winter air temperature and air pressure (the size and color of the vector arrow represent the wind speed, and the direction of the arrow represents the wind direction; red line represents the air temperature, and the blue line represents the air pressure; the red boxes in summer data represent TCs, and the blue boxes in winter data represent CWs).</p>
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<p>Alongshore current velocity at stations W1 (<b>a</b>) and W2 (<b>b</b>); cross-shore current velocity at stations W1 (<b>c</b>) and W2 (<b>d</b>); echo intensity at stations W1 (<b>e</b>) and W2 (<b>f</b>) (the black dashed line represents the instrument change time; the white area represents the missing data; the magenta line represents the residual water level (RWL); the blue line represents the alongshore wind speed (AW); the black line represents the bottom-water temperature (BWT); and the red boxes represent the TC events).</p>
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<p>(<b>a</b>) Alongshore current velocity at stations W1 and W2. (<b>b</b>) cross-shore current velocity at stations W1 and W2. (<b>c</b>) echo intensity at stations W1 and W2 (the black dashed line represents the instrument change time; the white area represents the missing data; the magenta line represents the residual water level (RWL); the blue line represents the alongshore wind speed (AW); the black line represents the bottom-water temperature (BWT); and the blue boxes represent the CW events).</p>
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<p>Alongshore residual current velocity at stations W1 (<b>a</b>) and W2 (<b>b</b>) in summer; cross-shore residual current velocity at stations W1 (<b>c</b>) and W2 (<b>d</b>) in summer (the red boxes represent the TC events).</p>
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<p>Alongshore residual current velocity at stations W1 (<b>a</b>) and W2 (<b>c</b>) in winter; cross-shore residual current velocity at stations W1 (<b>b</b>) and W2 (<b>d</b>) in winter (the blue boxes represent the CW events; the black dashed line represents the instrument change time).</p>
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<p>Wavelet analysis transform of alongshore surface current at station W2 in summer. (<b>a</b>) Measured current CWT; (<b>b</b>) residual current CWT; (<b>c</b>) WTC of the wind and surface current; (<b>d</b>) XWT of the wind and surface current (the thick lines represent areas that have passed a 95% significance level test. The colors of the subfigure represent the signal energy. The relative phase relationship is also depicted in the last two panels with in-phase pointing to the right and anti-phase pointing to the left, and if the former leads the latter by 90°, it will point straight downward. The former represents wind, and the latter represents the current).</p>
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<p>Wavelet analysis transform of alongshore surface current at stations W1 and W2 in winter. (<b>a</b>) Measured current CWT; (<b>b</b>) residual current CWT; (<b>c</b>) WTC of the wind and surface current; (<b>d</b>) XWT of the wind and surface current (the thick lines represent areas that have passed a 95% significance level test. The colors of the subfigure represent the signal energy. The relative phase relationship is also depicted in the last two panels with in-phase pointing to the right and anti-phase pointing to the left, and if the former leads the latter by 90°, it will point straight downward. The former represents wind, and the latter represents the current).</p>
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<p>Ekman volume transport composite distribution in the NSCS. (<b>a</b>) During T1; (<b>b</b>) relaxation stage of TCs; (<b>c</b>) during T2; (<b>d</b>) during C1; (<b>e</b>) relaxation stage of CWs; (<b>f</b>) during C2; (<b>g</b>) Ekman volume transport curve in the study area. The red circles represent the TC circles; white lines represent the TC tracks; red boxes represent the TCs; and blue boxes represent the CWs.</p>
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<p>Schematic of impacts of TCs and CWs on coastal marine environment in the NSCS. (<b>a</b>) T1 and T2 represent different tracks; red and yellow circles represent the radius of T1 and T2, respectively; the black arrows represent the mixing caused by wind stress. (<b>b</b>) C1, C2, and C3 represent the different intensities of the CW; the blue arrow and wind direction symbol represent the CW direction and wind speed. The horizontal background color represents the water depth. Water depth data were obtained from the ETOPO Global Relief Model (public access).</p>
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17 pages, 16180 KiB  
Article
Net Primary Production Simulation and Influencing Factors Analysis of Forest Ecosystem Based on a Process-Based Model
by Zhu Yang, Xuanrui Huang, Yunxian Qing, Hongqian Li, Libin Hong and Wei Lu
Appl. Sci. 2024, 14(23), 10912; https://doi.org/10.3390/app142310912 - 25 Nov 2024
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Abstract
Accurate assessment of net primary production (NPP) can truly reflect the carbon budget balance of the forest ecosystem. In this study, the boreal ecosystem productivity simulation (BEPS) model was used to simulate the NPP of Saihanba mechanized forest farm in 2020, and the [...] Read more.
Accurate assessment of net primary production (NPP) can truly reflect the carbon budget balance of the forest ecosystem. In this study, the boreal ecosystem productivity simulation (BEPS) model was used to simulate the NPP of Saihanba mechanized forest farm in 2020, and the influencing factors of NPP were analyzed. The meteorological, forest cover, leaf area index (LAI) and other data required for the model, as well as the data for verifying, were from field surveys or downloaded from different sources. The results showed that: (1) Within the scale of the flux tower, the diurnal variation of NPP reached a maximum in June. The monthly average peak value of latent heat flux was in June, and the sensible heat flux was in March. The temperature of the understory canopy was mostly higher than that of the overstory canopy and air temperature. (2) At the regional scale, the total NPP in the study area in 2020 was 4.25 × 1011 g C a−1, with an average of 564.71 g C m−2 a−1. The annual average NPP of silver birch (Betula platyphylla) was the largest, and the total NPP of northern Chinese larch (Larix principis-ruprechtii) was the largest. (3) NPP was highly sensitive to LAI. Topographic factors had effects on NPP. The average value of NPP was relatively high in the shady slope and the gentle slope. Full article
(This article belongs to the Special Issue GIS-Based Environmental Monitoring and Analysis)
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<p>Location of the study area and the flux tower.</p>
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<p>Land cover types.</p>
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<p>Topographic factor maps of the study area: (<b>a</b>) DEM data; (<b>b</b>) the slope map; (<b>c</b>) the slope aspect map.</p>
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<p>Model structural theory process.</p>
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<p>Schematic diagram of radiation transmission.</p>
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<p>Simulated NPP of the flux tower in 2020: (<b>a</b>) Daily NPP; (<b>b</b>) monthly NPP.</p>
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<p>Monthly averaged daily variation of simulated heat flux of the flux tower.</p>
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<p>Annual average daily variation of air temperature and simulated canopy temperature of the flux tower.</p>
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<p>NPP distribution of the study area in 2020.</p>
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<p>Impact of topographic factors on NPP. (<b>a</b>) Altitude; (<b>b</b>) slope; (<b>c</b>) aspect.</p>
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<p>Regression analysis of estimated and MODIS NPP.</p>
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30 pages, 13659 KiB  
Article
Spatial Gap-Filling of Himawari-8 Hourly AOD Products Using Machine Learning with Model-Based AOD and Meteorological Data: A Focus on the Korean Peninsula
by Youjeong Youn, Seoyeon Kim, Seung Hee Kim and Yangwon Lee
Remote Sens. 2024, 16(23), 4400; https://doi.org/10.3390/rs16234400 - 25 Nov 2024
Viewed by 189
Abstract
Given the complex spatiotemporal variability of aerosols, high-frequency satellite observations are essential for accurately mapping their distribution. However, optical remote sensing encounters difficulties in detecting Aerosol Optical Depth (AOD) over cloud-covered regions, creating data gaps that limit comprehensive environmental analysis. This study introduces [...] Read more.
Given the complex spatiotemporal variability of aerosols, high-frequency satellite observations are essential for accurately mapping their distribution. However, optical remote sensing encounters difficulties in detecting Aerosol Optical Depth (AOD) over cloud-covered regions, creating data gaps that limit comprehensive environmental analysis. This study introduces a spatial gap-filling method for Himawari-8/Advanced Himawari Imager (AHI) hourly AOD data, using a Random Forest (RF) model that integrates meteorological variables and model-based AOD data. Developed and validated over South Korea from 1 January to 31 December 2019, the model effectively improved data coverage from 6% to 100%. The approach demonstrated high performance in blind tests, achieving a root mean square error (RMSE) of 0.064 and a correlation coefficient (CC) of 0.966. Meteorological analysis indicated optimal model performance under cold, dry conditions (RMSE: 0.047, CC: 0.956), compared to humid conditions (RMSE: 0.105, CC: 0.921). Validation against Aerosol Robotic Network (AERONET) ground observations showed that, while the original Himawari-8 data exhibited higher accuracy (RMSE: 0.189, CC: 0.815, n = 346), the gap-filled dataset maintained reasonable precision (RMSE: 0.208, CC: 0.711) and significantly increased the number of valid data points (n = 4149). Furthermore, the gap-filled dataset successfully captured seasonal AOD patterns, with values ranging from 0.245–0.300 in winter to 0.381–0.391 in summer, providing a comprehensive view of aerosol dynamics across South Korea. Full article
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<p>Examples of converting 3-hourly to hourly data using cubic spline interpolation for meteorological variables: (<b>a</b>) before and after temporal interpolation for the TMP on 1 March 2019 and (<b>b</b>) before and after temporal interpolation for the RH on 1 March 2019. The top row in each panel (<b>a</b>,<b>b</b>) shows the raw 3-hourly data, while the bottom row displays the interpolated hourly data. Each column represents a specific UTC time (00 to 09). The color scale indicates the intensity of the variables, with TMP in °C and RH in %. The interpolation process fills the temporal gaps between the 3-hourly observations, resulting in a continuous hourly dataset that matches the temporal resolution of the Himawari-8/AHI AOD product. Notably, the smooth transitions in values over time are evident in the interpolated data, particularly in the previously empty time slots (01, 02, 04, 05, 07, and 08 UTC).</p>
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<p>Schematic diagram of the RF model used for gap-filling the Himawari-8/AHI 1-hourly AOD product. The model integrates LDAPS meteorological variables (TMP, U_WS, V_WS, BLH, LHFL, HCDC, RH, DSSF, PRES, DPT) and model-based AOD data (CAMS, MERRA-2) as input features. The output is the predicted AOD (AOD Pred), which is compared with the AHI AOD for quality assurance. Only AHI AOD data classified as “very good” quality were used for model training and validation. Solid lines represent the flow and processing of data, while dashed lines indicate comparisons with reference data.</p>
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<p>Schematic representation of the model validation process: The validation process includes a training set used for 5-fold CV to tune hyperparameters and a separate test set for final evaluation. The training set is divided into five subsets for CV, with each subset serving as a validation set once, while the remaining four subsets are used for training. The test set is kept entirely separate to independently evaluate the model’s performance in the final step.</p>
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<p>Density scatter plots comparing observed versus predicted AHI hourly AOD values using the gap-filling model with all features for (<b>a</b>) the 5-fold CV set (n = 433,286) and (<b>b</b>) the blind test set (n = 100,000). The color scale represents the number of data points per pixel, with warmer colors indicating higher densities. The 1:1 line (indicating perfect prediction) is in black, while the red line represents the fitted regression line. Statistical metrics (MBE, MAE, RMSE, CC) and the fitted line equations are provided in the top left corner of each plot.</p>
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<p>Difference in Correlation Coefficient (CC) between the entire test dataset and the subsets divided by value ranges. A higher CC is observed for (<b>a</b>) the entire test dataset, while lower CC values are observed for (<b>b</b>) the low-value group, (<b>c</b>) the medium-value group, and (<b>d</b>) the high-value group. Black circles represent the portions of data corresponding to each group, while gray ellipses show the entirety of the data.</p>
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<p>Geographical distribution of the six AERONET sites used for validation in South Korea. The sites include Gangneung_WNU (forest-adjacent), Seoul_SNU (urban), Hankuk_UFS (forest-adjacent), Anmyon (forest), and Gwangju_GIST (urban). The map illustrates the diverse environmental settings of these sites, covering urban areas, forests, and coastal regions across the Korean Peninsula.</p>
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<p>Scatter plots comparing (<b>a</b>) original Himawari-8 AOD data (only matched pairs between Himawari-8 and AERONET observations) and (<b>b</b>) gap-filled AOD data (only predicted values from the gap-filling model, excluding original Himawari-8 data) against AERONET AOD observations. Plot (<b>a</b>) was represented as a scatter plot because of smaller samples (n = 346), whereas plot (<b>b</b>) was illustrated as a density plot due to larger sample size (n = 4149) with blue tones indicating higher densities. The 1:1 line is shown in black. Statistical metrics, including MBE, MAE, RMSE, and CC, are also provided in the top left corner.</p>
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<p>Variable importance of the RF model for AOD gap-filling.</p>
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<p>Comparison of daily MERRA-2 and CAMS AOD values for 2019, with the dashed red line representing the 1:1 line.</p>
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<p>Monthly maps of gap-filled Himawari-8/AHI AOD for the year 2019, illustrating the spatial distribution of AOD values (ranging from 0 to 1) for each month. These maps provide a comprehensive view of the seasonal and regional variations in AOD throughout the year.</p>
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<p>Monthly maps of gap-filled Himawari-8/AHI AOD for the year 2019, illustrating the spatial distribution of AOD values (ranging from 0 to 1) for each month. These maps provide a comprehensive view of the seasonal and regional variations in AOD throughout the year.</p>
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<p>Time series comparison of Himawari-8 gap-filled AOD (purple) and AERONET AOD (brown) measurements during 16–22 March 2019, at different sites in South Korea: (<b>a</b>) Anmyon representing a forest environment, (<b>b</b>) Seoul_SNU representing an urban environment, and (<b>c</b>) Hankuk_UFS representing a near-forest environment. The middle panels (19 March) highlight the model’s performance during the high-concentration event, while the surrounding dates demonstrate its capability to capture typical conditions.</p>
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<p>Representative examples of hourly AOD gap-filling results for 2019, showing sample sets from each of the 12 months (January to December) to reflect different seasonal patterns. Each row displays 8 consecutive hours (00–07 UTC) of AOD data for a selected date. The “Before” rows show the original AOD data with gaps, while the “After” rows present the gap-filled data. A color scale indicates AOD values, ranging from 0 (blue) to 1 (red).</p>
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<p>Representative examples of hourly AOD gap-filling results for 2019, showing sample sets from each of the 12 months (January to December) to reflect different seasonal patterns. Each row displays 8 consecutive hours (00–07 UTC) of AOD data for a selected date. The “Before” rows show the original AOD data with gaps, while the “After” rows present the gap-filled data. A color scale indicates AOD values, ranging from 0 (blue) to 1 (red).</p>
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<p>Representative examples of hourly AOD gap-filling results for 2019, showing sample sets from each of the 12 months (January to December) to reflect different seasonal patterns. Each row displays 8 consecutive hours (00–07 UTC) of AOD data for a selected date. The “Before” rows show the original AOD data with gaps, while the “After” rows present the gap-filled data. A color scale indicates AOD values, ranging from 0 (blue) to 1 (red).</p>
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18 pages, 8151 KiB  
Article
Projections of Climate Change Impact on Stream Temperature: A National-Scale Assessment for Poland
by Paweł Marcinkowski
Appl. Sci. 2024, 14(23), 10900; https://doi.org/10.3390/app142310900 - 25 Nov 2024
Viewed by 186
Abstract
This national-scale assessment explores the anticipated impact of climate change on stream temperature in Poland. Utilizing an ensemble of six EURO-CORDEX projections (2006 to 2100) under Representative Concentration Pathways (RCPs) 4.5 and 8.5, the study employs the Soil and Water Assessment Tool (SWAT) [...] Read more.
This national-scale assessment explores the anticipated impact of climate change on stream temperature in Poland. Utilizing an ensemble of six EURO-CORDEX projections (2006 to 2100) under Representative Concentration Pathways (RCPs) 4.5 and 8.5, the study employs the Soil and Water Assessment Tool (SWAT) to simulate stream temperature regimes. Validation against observed stream temperatures at 369 monitoring points demonstrates the reliability and accuracy of the SWAT model performance. Projected changes in air temperature reveal distinct seasonal variations and emission scenario dependencies. The validated stream temperature model indicates a uniform warming tendency across Poland, emphasizing the widespread nature of climate change impacts on aquatic ecosystems. Results show an increase in country-averaged stream temperature from the baseline (16.1 °C), with a rise of 0.5 °C in the near future (NF) and a further increase by 1 °C in the far future (FF) under RCP4.5. Under RCP8.5, the increase is more pronounced, reaching 1 °C in the NF and a substantial 2.6 °C in the FF. These findings offer essential insights for environmental management, emphasizing the need for adaptive strategies to mitigate adverse effects on freshwater ecosystems. However, as a preliminary study, this work uses a simplified temperature model that does not account for detailed hydrological processes and spatial variability, making it a good starting point for more detailed future research. Full article
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<p>Study location with SWAT sub-basins (<b>A</b>), stream temperature gauging stations (<b>B</b>), and mean seasonal air temperatures in summer (<b>C</b>) and winter (<b>D</b>).</p>
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<p>Country-averaged monthly changes in mean daily air temperature under RCP4.5 (blue) and RCP8.5 (orange). The intensity of each colour represents different horizons: light (baseline—ACT), medium (near future—NF), and dark (far future—FF).</p>
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<p>Goodness-of-fit measures derived upon validation: Kling–Gupta efficiency (KGE) (<b>A</b>), percent bias (PBIAS) (<b>B</b>), and coefficient of determination (R<sup>2</sup>) (<b>C</b>).</p>
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<p>Box plots showing the model performance expressed by Kling–Gupta efficiency (KGE), coefficient of determination (R2) (<b>A</b>), and percent bias (PBIAS) (<b>B</b>) values in 369 water quality monitoring points.</p>
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<p>Spatial distribution of multi-annual summer season mean stream temperature at the reach level for Representative Concentration Pathways (RCPs) 4.5 and 8.5 at baseline (ACT), in the near future (NF), and in the far future (FF).</p>
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<p>Spatial distribution of multi-annual winter season mean stream temperature at the reach level for Representative Concentration Pathways (RCPs) 4.5 and 8.5 at baseline (ACT), in the near future (NF), and in the far future (FF).</p>
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<p>Projections of the average daily air temperature during the summer period over multiple years for RCP4.5 (<b>A</b>) and RCP8.5 (<b>B</b>). The bands indicate extreme values (min and max) from nine climate models; the solid line represents the median. The green colour represents the historical period. The intensity of the blue and orange colours denotes the time horizon, where lighter shades indicate the near future, while darker shades indicate the far future.</p>
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<p>Projections of the average daily air temperature during the winter period over multiple years for RCP4.5 (<b>A</b>) and RCP8.5 (<b>B</b>). The bands indicate extreme values (min and max) from nine climate models; the solid line represents the median. The green colour represents the historical period. The intensity of the blue and orange colours denotes the time horizon, where lighter shades indicate the near future, while darker shades indicate the far future.</p>
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23 pages, 2816 KiB  
Article
Improving Flood Streamflow Estimation of Ungauged Small Reservoir Basins Using Remote Sensing and Hydrological Modeling
by Fangrong Zhou, Nan Wu, Yuning Luo, Yuhao Wang, Yi Ma, Yifan Wang and Ke Zhang
Remote Sens. 2024, 16(23), 4399; https://doi.org/10.3390/rs16234399 - 24 Nov 2024
Viewed by 415
Abstract
Small- and medium-sized reservoirs significantly alter natural flood processes, making it essential to understand their impact on runoff for effective water resource management. However, the lack of measured data for most small reservoirs poses challenges for accurately simulating their behavior. This study proposes [...] Read more.
Small- and medium-sized reservoirs significantly alter natural flood processes, making it essential to understand their impact on runoff for effective water resource management. However, the lack of measured data for most small reservoirs poses challenges for accurately simulating their behavior. This study proposes a novel method that utilizes readily available satellite observation data, integrating hydraulic, hydrological, and mathematical formulas to derive outflow coefficients. Based on the Grid-XinAnJiang (GXAJ) model, the enhanced GXAJ-R model accounts for the storage and release effects of ungauged reservoirs and is applied to the Tunxi watershed. Results show that the original GXAJ model achieved a stable performance with an average NSE of 0.88 during calibration, while the NSE values of the GXAJ and GXAJ-R models during validation ranged from 0.78 to 0.97 and 0.85 to 0.99, respectively, with an average improvement of 0.03 in the GXAJ-R model. This enhanced model significantly improves peak flow simulation accuracy, reduces relative flood peak error by approximately 10%, and replicates the flood flow process with higher fidelity. Additionally, the area–volume model derived from classified small-scale data demonstrates high accuracy and reliability, with correlation coefficients above 0.8, making it applicable to other ungauged reservoirs. The OTSU-NDWI method, which improves the NDWI, effectively enhances the accuracy of water body extraction from remote sensing, achieving overall accuracy and kappa coefficient values exceeding 0.8 and 0.6, respectively. This study highlights the potential of integrating satellite data with hydrological models to enhance the understanding of reservoir behavior in data-scarce regions. It also suggests the possibility of broader applications in similarly ungauged basins, providing valuable tools for flood management and risk assessment. Full article
(This article belongs to the Special Issue Remote Sensing for Terrestrial Hydrologic Variables)
14 pages, 8923 KiB  
Article
Thermoregulation and Soil Moisture Management in Strawberry Cultivation Mulched with Sheep Wool
by Jan Broda, Andrzej Gawłowski, Monika Rom, Tomasz Kukulski and Katarzyna Kobiela-Mendrek
Appl. Sci. 2024, 14(23), 10884; https://doi.org/10.3390/app142310884 - 24 Nov 2024
Viewed by 414
Abstract
The application of wool as mulch in strawberry cultivation was analysed to find a solution for the rational use of wool from mountain sheep. In the plantation, the experimental plots mulched with wool, straw, and bark were appointed. The plots were monitored during [...] Read more.
The application of wool as mulch in strawberry cultivation was analysed to find a solution for the rational use of wool from mountain sheep. In the plantation, the experimental plots mulched with wool, straw, and bark were appointed. The plots were monitored during the experiment, while the soil temperature and moisture content were measured. The data collected in two-hour intervals were analysed, taking into account air temperature and falls registered in the local meteorological station. Additionally, the progress of mulch biodegradation was tracked. The changes in the wool morphology that occurred by biodegradation were observed during microscopic examinations using the Scanning Electron Microscope (SEM). It was stated that wool mulch plays an essential role in thermoregulation of the soil surface, prevents the overheating of the soil during the summer heat, and protects soil against excessive cooling during cold nights. The wool mulch minimizes the fluctuations between the soil’s day and night temperature. The fluctuations do not exceed 2–3 degrees on hot summer days, which are five times smaller than for the control plot. The wool retains large amounts of rainwater several times its weight. The water is then slowly released, providing the growing plants with a moist environment during a longer rainless period. Moreover, wool is difficult to biodegrade and maintains its properties for a long time, lasting longer than one vegetation season. Compared to straw and bark, the temperature fluctuations recorded for wool are two times smaller, and its effectiveness in water management is considerably better. The beneficial impact of the wool mulch ensuring favourable conditions for strawberry growth was explained by the specific wool structure and its unique properties. Full article
(This article belongs to the Section Materials Science and Engineering)
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<p>The experimental plot mulched with various materials in a strawberry plantation: (<b>a</b>) control without mulch wool; (<b>b</b>) wool; (<b>c</b>) straw; (<b>d</b>) bark.</p>
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<p>Daily temperature graph during June 2023; (<b>a</b>) the air temperature measured in the local meteorological station; (<b>b</b>) soil temperature recorded for experimental plots.</p>
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<p>The daily difference in soil temperature for plots mulched with various materials in June 2023.</p>
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<p>Daily temperature graph during January 2024; (<b>a</b>) the air temperature measured in the local meteorological station; (<b>b</b>) soil temperature recorded for experimental plots.</p>
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<p>Daily temperature graph during January 2024; (<b>a</b>) the air temperature measured in the local meteorological station; (<b>b</b>) soil temperature recorded for experimental plots.</p>
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<p>The daily difference in soil temperature for plots mulched with various materials in January 2024.</p>
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<p>Daily rainfall and soil moisture during June 2023; (<b>a</b>) the fall registered in the meteorological station; (<b>b</b>) the soil moisture for experimental plots.</p>
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<p>Daily rainfall and soil moisture during June 2023; (<b>a</b>) the fall registered in the meteorological station; (<b>b</b>) the soil moisture for experimental plots.</p>
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<p>Daily rainfall and soil moisture during January 2024; (<b>a</b>) the fall registered in the meteorological station; (<b>b</b>) the soil moisture for experimental plots.</p>
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<p>The morphology of the mountain sheep wool; (<b>a</b>) scales occurring on the fibre’s surface; (<b>b</b>) the cross-section of medullated fibres.</p>
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<p>The development of fungi in the wool mulch in October 2023: (<b>a</b>) fungi colonised on the surface of the fibres; (<b>b</b>) the mycelium located between fibres.</p>
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<p>The biological decomposition of wool fibres; (<b>a</b>) the system of interconnected channels and pores; (<b>b</b>) the deep cavity extended through all wool layers.</p>
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27 pages, 7384 KiB  
Article
Constructing the Joint Probability Spatial Distribution of Different Levels of Drought Risk Based on Copula Functions: A Case Study in the Yellow River Basin
by Quanwei Wang, Yimin Wang, Chen Niu and Mengdi Huang
Water 2024, 16(23), 3374; https://doi.org/10.3390/w16233374 - 24 Nov 2024
Viewed by 217
Abstract
Joint multivariate distribution and calculation of return period are essential in enhancing drought risk assessment and promoting the sustainable development of water resources. Aiming to address the increasingly serious drought situation in the Yellow River Basin, this study first utilized the Soil and [...] Read more.
Joint multivariate distribution and calculation of return period are essential in enhancing drought risk assessment and promoting the sustainable development of water resources. Aiming to address the increasingly serious drought situation in the Yellow River Basin, this study first utilized the Soil and Water Assessment Tool (SWAT) distributed hydrological model combined with the Standardized Precipitation Evapotranspiration Index (SPEI), the Standardized Soil Moisture Index (SSMI), and the Standard Water Yield Index (SWYI); the duration, peak, and severity of meteorological, agricultural, and hydrological droughts were analyzed. Based on the selected copula function, a three-dimensional joint distribution of drought duration (D), drought severity (S), and maximum severity (M) was constructed. The corresponding copula joint probability was calculated, leading to the three-dimensional joint return period and concurrent return period of meteorological drought, agricultural drought, and hydrological drought. The findings reveal several key trends: (1) Meteorological drought intensifies over time. Although drought areas eased after the 1990s, the overall drought trend continues to rise. Agricultural drought has intensified in arid regions but eased in semi-humid areas after the 2000s. Hydrological drought was severe in the upstream regions during the 1990s but eased in the 2000s, while it was particularly severe in the midstream and downstream regions during the 2000s. (2) Meteorological droughts are more severe in arid and semi-arid temperate regions and milder in semi-humid cold temperate regions. Agricultural droughts are extreme in arid and semi-arid cold temperate regions. Hydrological drought events are fewer but more severe in semi-arid temperate regions and have the lowest probability of occurrence in semi-humid cold temperate regions. (3) The overall probability of the occurrence of meteorological drought is between 55.7% and 69%; that of agricultural drought is between 73.1% and 91.7%, and that of hydrological drought is between 66.9% and 84%. Drought risk assessment provides scientific references for the analysis of the uncertainty of water supply in the basin and the formulation of effective risk management strategies. Full article
19 pages, 5835 KiB  
Article
A Case Study on the Impact of Boundary Layer Turbulence on Convective Clouds in the Eastern Margin of the Tibetan Plateau
by Ting Wang, Maoshan Li, Yonghao Jiang, Yuchen Liu, Ming Gong, Shaoyang Wang, Peng Sun, Yaoming Ma and Fanglin Sun
Remote Sens. 2024, 16(23), 4376; https://doi.org/10.3390/rs16234376 - 23 Nov 2024
Viewed by 225
Abstract
In this study, we utilized ECMWF Reanalysis of the Global Climate at Atmospheric Resolution 5 (ERA5) data, FengYun-4B satellite (FY-4B) data, a Wind3D 6000 Three-Dimensional Scanning Laser Wind Radar, and raindrop spectrum data to analyze the circulation background, convective cloud changes, boundary layer [...] Read more.
In this study, we utilized ECMWF Reanalysis of the Global Climate at Atmospheric Resolution 5 (ERA5) data, FengYun-4B satellite (FY-4B) data, a Wind3D 6000 Three-Dimensional Scanning Laser Wind Radar, and raindrop spectrum data to analyze the circulation background, convective cloud changes, boundary layer wind field variations, and precipitation drop size spectrum characteristics of a severe convective rainfall process that occurred on 3 April 2024 in the eastern margin of the Tibetan Plateau. The findings indicated the following: (1) The rain belt of this precipitation event showed a southwest–northeast trend. During the vigorous development of convection, the rainfall intensity and total precipitation at the station increased, with a wider raindrop spectrum, and the raindrop spectrum of this precipitation process was unimodal. (2) On 3 April, the interaction between the eastward movement of the plateau trough at 500 hPa and the upper-level jet stream at 200 hPa in the eastern Tibetan Plateau and the Sichuan Basin area, along with the necessary conditions for precipitation, such as energy and moisture, led to severe convective rainfall. (3) This intense convective precipitation process was caused by the vigorous convective clouds that developed in the eastern part of the Tibetan Plateau. As these clouds developed and moved eastward out of the plateau, they precipitated with increased turbulence intensity at the station, leading to the generation of intense convective activities at the site. (4) One hour before the precipitation, there were significant increases in horizontal wind speed, vertical air velocity, and turbulence intensity within the boundary layer, and there were also significant changes in the horizontal wind direction. The results obtained can provide important theoretical references for the prediction of severe convective rainfall and the performance of numerical simulations thereon. Full article
(This article belongs to the Section Atmospheric Remote Sensing)
20 pages, 11913 KiB  
Article
Long-Term Spatiotemporal Analysis of Precipitation Trends with Implications of ENSO-Driven Variability in the Department of Magdalena, Colombia
by Geraldine M. Pomares-Meza, Yiniva Camargo Caicedo and Andrés M. Vélez-Pereira
Water 2024, 16(23), 3372; https://doi.org/10.3390/w16233372 - 23 Nov 2024
Viewed by 342
Abstract
The Magdalena department, influenced by southern trade winds and ocean currents from the Atlantic and Pacific, is a climatically vulnerable region. This study assesses the Magdalena Department’s precipitation trends and stationary patterns by analyzing multi-year monthly records from 55 monitoring stations from 1990 [...] Read more.
The Magdalena department, influenced by southern trade winds and ocean currents from the Atlantic and Pacific, is a climatically vulnerable region. This study assesses the Magdalena Department’s precipitation trends and stationary patterns by analyzing multi-year monthly records from 55 monitoring stations from 1990 to 2022. To achieve this, the following methods were used: (i) homogeneous regions were established by an unsupervised clustering approach, (ii) temporal trends were quantified using non-parametric tests, (iii) stationarity was identified through Morlet wavelet decomposition, and (iv) Sea Surface Temperature (SST) in four Niño regions was correlated with stationarity cycles. Silhouette’s results yielded five homogeneous regions, consistent with the National Meteorological Institute (IDEAM) proposal. The Department displayed decreasing annual trends (−32–−100 mm/decade) but exhibited increasing monthly trends (>20 mm/decade) during the wettest season. The wavelet decomposition analysis revealed quasi-bimodal stationarity, with significant semiannual cycles (~4.1 to 5.6 months) observed only in the eastern region. Other regions showed mixed behavior: non-stationary in the year’s first half and stationary in the latter half. Correlation analysis showed a significant relationship between SST in the El Niño 3 region (which accounted for 50.5% of the coefficients), indicating that strong phases of El Niño anticipated precipitation responses for up to six months. This confirms distinct rainfall patterns and precipitation trends influenced by the El Niño–Southern Oscillation (ENSO), highlighting the need for further hydrometeorological research in the area. Full article
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<p>General location, physiographic units, and hydrometeorological station network of the Department of Magdalena (map on the left), detailing the spatial distribution of average annual precipitation in the Department of Magdalena (1990–2022) (map on the right).</p>
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<p>The conceptual framework of the proposed methodology.</p>
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<p>Comparison between clustering scenarios. The size of the points is proportional to the average Silhouette coefficient (average cluster performance), and the transparency level indicates the individual Silhouette coefficient (station affinity to the cluster’s centroid). Sites indicated by empty symbols represent the centroid for each cluster. (<b>A</b>) Euclidean + non-standardization scenario. (<b>B</b>) Euclidean + z-score scenario (selected scenario). (<b>C</b>) DTW + non-standardization scenario. (<b>D</b>) DTW + z-score scenario.</p>
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<p>Spatial distribution of total annual rainfall in the final configuration of homogeneous regions in the Magdalena department.</p>
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<p>Results by type of trend (direction of the triangle), statistical significance (size of the triangle), and value of the magnitude of change in mm decade<sup>−1</sup> (color scale) of total annual rainfall (map on the left) and total monthly rainfall (small maps on the right) in the Magdalena department.</p>
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<p>Results by type of trend (direction of the triangle), statistical significance (size of the triangle), and value of the magnitude of change in day/decade (color scale) of total annual rainy days (map on the left) and total monthly rainy days (small maps on the right) in the Magdalena department.</p>
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<p>Distribution of wavelet power across homogeneous rainfall regions in the Magdalena department. For all scalograms, the x-axis represents the time component, and the y-axis represents the scale component, whose limits were adjusted from a 3- to a 120-month (10-year) scale. The color scale indicates wavelet power variation and represents each time-scale component’s contribution to the rainfall series’ variance. Black crosses delimit the regions of significant stationarity, calculated using the Torrence and Compo [<a href="#B72-water-16-03372" class="html-bibr">72</a>] proposed test at a 5% significance level.</p>
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<p>Wavelet coherence (<b>left</b>) and phase difference (<b>right</b>) between multi-year precipitation and average SST in the El Niño 3 region. For all scalograms, the x-axis represents the time component (1990–2022), and the y-axis represents the scale component, whose limits were adjusted from a 3- to 120-month (i.e., 10-year) scale. The color scale indicates wavelet coherence and phase difference variation and represents both parameters’ correlation and synchronization (respectively) at the specific time-scale component. Significant correlation at a 5% significance level is represented by dashed black lines, indicating the periods most likely influenced by SST seasonality in their corresponding cycle length.</p>
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<p>Comparison between (<b>A</b>) Thornthwaite moisture index classification proposed by IDEAM (2017) and (<b>B</b>) clustering-based precipitation regionalization in the department of Magdalena.</p>
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20 pages, 1125 KiB  
Article
Energy Dissipation Assessment in Flow Downstream of Rectangular Sharp-Crested Weirs
by Hossein Sohrabzadeh Anzani, Sameh Ahmed Kantoush, Ali Mahdian Khalili and Mehdi Hamidi
Water 2024, 16(23), 3371; https://doi.org/10.3390/w16233371 - 23 Nov 2024
Viewed by 200
Abstract
Sharp-crested weirs are commonly used in hydraulic engineering for flow measurement and control. Despite extensive research on sharp-crested weirs, particularly regarding their discharge coefficients, more information is needed via research on their energy dissipation downstream. This study conducted experimental tests to assess the [...] Read more.
Sharp-crested weirs are commonly used in hydraulic engineering for flow measurement and control. Despite extensive research on sharp-crested weirs, particularly regarding their discharge coefficients, more information is needed via research on their energy dissipation downstream. This study conducted experimental tests to assess the influence of contraction ratio (b/B) of rectangular sharp-crested weirs (RSCWs) on energy dissipation downstream under free flow conditions. Five RSCWs with different b/B equals 6/24, 7/24, 8/24, 9/24, and 10/24 were used. The results showed a consistent decrease in relative energy dissipation (Δ𝐸𝑟) with an increase in the head over the weir. Furthermore, as the discharge per unit width (q) increased, the relative energy dissipation (Δ𝐸𝑟) decreased, indicating more efficient discharge over the weir. A higher b/B further reduces Δ𝐸𝑟, suggesting that wider weirs are more effective in minimizing energy losses. The maximum relative residual energy (E1/E0) and relative energy dissipation (Δ𝐸𝑟) occurred at b/B = 10/24 and 6/24, with values of 0.825 and 0.613, respectively. Additionally, the maximum discharge coefficient (Cd) of RSCWs is found at b/B = 6/24, with an average value of 0.623. The results support the accuracy of the proposed equation with R2 = 0.988, RMSE = 0.0083, and MAPE = 1.43%. Full article
(This article belongs to the Section Hydraulics and Hydrodynamics)
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