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Search Results (1,169)

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19 pages, 8430 KiB  
Article
Spatiotemporal Variation of Water Use Efficiency and Its Responses to Climate Change in the Yellow River Basin from 1982 to 2018
by Jie Li, Fen Qin, Yingping Wang, Xiuyan Zhao, Mengxiao Yu, Songjia Chen, Jun Jiang, Linhua Wang and Junhua Yan
Remote Sens. 2025, 17(2), 316; https://doi.org/10.3390/rs17020316 - 17 Jan 2025
Viewed by 231
Abstract
The ecosystem water use efficiency (WUE) plays a critical role in many aspects of the global carbon cycle, water management, and ecological services. However, the response mechanisms and driving processes of WUE need to be further studied. This research was conducted based on [...] Read more.
The ecosystem water use efficiency (WUE) plays a critical role in many aspects of the global carbon cycle, water management, and ecological services. However, the response mechanisms and driving processes of WUE need to be further studied. This research was conducted based on Gross Primary Productivity (GPP), Evapotranspiration (ET), meteorological station data, and land use/cover data, and the methods of Ensemble Empirical Mode Decomposition (EEMD), trend variation analysis, the Mann–Kendall Significant Test (M-K test), and Partial Correlation Analysis (PCA) methods. Our study revealed the spatio-temporal trend of WUE and its influencing mechanism in the Yellow River Basin (YRB) and compared the differences in WUE change before and after the implementation of the Returned Farmland to Forestry and Grassland Project in 2000. The results show that (1) the WUE of the YRB showed a significant increase trend at a rate of 0.56 × 10−2 gC·kg−1·H2O·a−1 (p < 0.05) from 1982 to 2018. The area showing a significant increase in WUE (47.07%, Slope > 0, p < 0.05) was higher than the area with a significant decrease (14.64%, Slope < 0, p < 0.05). The region of significant increase in WUE in 2000–2018 (45.35%, Slope > 0, p < 0.05) was higher than that of 1982–2000 (8.23%, Slope > 0, p < 0.05), which was 37.12% higher in comparison. (2) Forest WUE (1.267 gC·kg−1·H2O) > Cropland WUE (0.972 gC·kg−1·H2O) > Grassland WUE (0.805 gC·kg−1·H2O) under different land cover types. Forest ecosystem WUE has the highest rate of increase (0.79 × 10−2 gC·kg−1·H2O·a−1) from 2000 to 2018. Forest ecosystem WUE increased by 0.082 gC·kg−1·H2O after 2000. (3) precipitation (37.98%, R > 0, p < 0.05) and SM (10.30%, R > 0, p < 0.05) are the main climatic factors affecting WUE in the YRB. A total of 70.39% of the WUE exhibited an increasing trend, which is mainly attributed to the simultaneous increase in GPP and ET, and the rate of increasing GPP is higher than the rate of increasing ET. This study could provide a scientific reference for policy decision-making on the terrestrial carbon cycle and biodiversity conservation. Full article
(This article belongs to the Special Issue Remote Sensing for Terrestrial Hydrologic Variables)
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<p>Study area, vegetation type, basin boundary, and elevation.</p>
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<p>Temporal trends of WUE in 1982–2018. (<b>a</b>) Annual; (<b>b</b>) Grow.</p>
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<p>Spatial variation characteristics of WUE in the YRB. (<b>a</b>) Annual WUE in 1982–2018; (<b>b</b>) Annual WUE in 1982–2000; (<b>c</b>) Annual WUE in 2000–2018; (<b>d</b>) Grow WUE in 1982–2018; (<b>e</b>) Annual WUE in 1982–2000; (<b>f</b>) Annual WUE in 2000–2018.</p>
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<p>Spatial characteristics of significant variation trend of the WUE in different time periods.</p>
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<p>Variation in WUE in different land cover types.</p>
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<p>The trends of WUE for different ecosystem types in the YRB. (<b>a</b>) Farmland; (<b>b</b>) Forest; (<b>c</b>) Grassland; (<b>d</b>) Other.</p>
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<p>Spatial distribution of partial correlation coefficient between WUE and climate factors in the YRB from 1982 to 2018. (<b>a</b>) WUE and temperature; (<b>b</b>) WUE and precipitation; (<b>c</b>) WUE and vapor pressure deficit; (<b>d</b>) WUE and soil moisture.</p>
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<p>Spatial distribution of partial correlation coefficient between WUE and climate factors in the YRB from 1982 to 2018 (significance test <span class="html-italic">p</span> &lt; 0.05). (<b>a</b>) WUE and temperature; (<b>b</b>) WUE and precipitation; (<b>c</b>) WUE and vapor pressure deficit; (<b>d</b>) WUE and soil moisture.</p>
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<p>WUE changes in response to GPP and ET across different time periods.</p>
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<p>WUE significant changes in response to GPP significant changes and ET significant changes across different time periods (significant test <span class="html-italic">p</span> &lt; 0.05).</p>
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23 pages, 6752 KiB  
Article
Development of Fractional Vegetation Cover Change and Driving Forces in the Min River Basin on the Eastern Margin of the Tibetan Plateau
by Shuyuan Liu, Li Zhou, Huan Wang, Jin Lin, Yuduo Huang, Peng Zhuo and Tianqi Ao
Forests 2025, 16(1), 142; https://doi.org/10.3390/f16010142 - 14 Jan 2025
Viewed by 356
Abstract
Fractional vegetation cover (FVC) is an important indicator of regional ecological environment change, and quantitative research on the spatial and temporal distribution of FVC and the trend of change is of great significance to the monitoring, evaluation, protection, and restoration of regional ecology. [...] Read more.
Fractional vegetation cover (FVC) is an important indicator of regional ecological environment change, and quantitative research on the spatial and temporal distribution of FVC and the trend of change is of great significance to the monitoring, evaluation, protection, and restoration of regional ecology. This study estimates the FVC of the eastern Tibetan Plateau margin from 2000 to 2020 using the image element dichotomous model based on the Google Earth Engine platform using MODIS-NDVI images. It also investigates the temporal and spatial changes of the FVC in this region and its drivers using the Theil–Sen and Mann–Kendall trend tests, spatial autocorrelation analysis, geodetector, and machine learning approaches impact. The results of this study indicated a generally erratic rising tendency, with the Min River Basin (MRB) near the eastern tip of the Tibetan Plateau having an annual average FVC of 0.67 and an annual growth rate of 0.16%. The percentage of places with better vegetation reached 60.37%. The regional FVC showed significant positive spatial autocorrelation and was clustered. Driver analyses showed that soil type, DEM, temperature, potential evapotranspiration, and land use type were the main drivers influencing FVC on the eastern margin of the Tibetan Plateau. In addition, the random forest (RF) model outperformed the support vector machine (SVM), backpropagation neural network (BP), and long short-term memory network (LSTM) in FVC regression fitting. In summary, this study shows that the overall FVC in the eastern margin of the Tibetan Plateau is on an upward trend, and the regional ecological environment has improved significantly over the past two decades. Full article
(This article belongs to the Section Forest Inventory, Modeling and Remote Sensing)
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<p>Location of the MRB study area, (<b>a</b>) Specific location on the Tibetan Plateau, (<b>b</b>) DEM, (<b>c</b>) Land use.</p>
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<p>Spatial distribution of the drivers in 2015.</p>
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<p>(<b>a</b>) Proportion of each FVC type from 2000 to 2020; (<b>b</b>) temporal trend of FVC variation.</p>
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<p>Spatial pattern of different classes of FVC on the eastern margin of the Tibetan Plateau, 2000–2020.</p>
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<p>FVC spatial transfer area distribution (<b>a</b>) from 2000 to 2010; (<b>b</b>) from 2010 to 2020.</p>
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<p>Trends in FVC and their significance.</p>
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<p>FVC global spatial autocorrelation.</p>
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<p>FVC localized spatial autocorrelation LISA aggregation distribution.</p>
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<p>FVC factor detection results.</p>
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<p>Interaction test results of vegetation cover drivers in different years (NE indicates nonlinear enhancement, BE indicates two-factor enhancement).</p>
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<p>Significance statistics for differences in the impact of each driver.</p>
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<p>Statistical findings for various FVC types or ranges for every factor.</p>
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<p>Comparison of true and regression values of FVC: (<b>a</b>) SVM, (<b>b</b>) BP, (<b>c</b>) LSTM, (<b>d</b>) RF.</p>
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17 pages, 2007 KiB  
Review
Enhancing Maize Production Through Timely Nutrient Supply: The Role of Foliar Fertiliser Application
by Brian Ssemugenze, Akasairi Ocwa, Ronald Kuunya, Costa Gumisiriya, Csaba Bojtor, János Nagy, Adrienn Széles and Árpád Illés
Agronomy 2025, 15(1), 176; https://doi.org/10.3390/agronomy15010176 - 13 Jan 2025
Viewed by 487
Abstract
Maize, regarded as a staple economic crop, attracts special global attention with the aim to enhance its production. Foliar fertilisation offers a complementary method to traditional soil fertilisation amongst resource-limited agricultural systems, providing a more efficient solution to nutrient deficiencies, especially in suboptimal [...] Read more.
Maize, regarded as a staple economic crop, attracts special global attention with the aim to enhance its production. Foliar fertilisation offers a complementary method to traditional soil fertilisation amongst resource-limited agricultural systems, providing a more efficient solution to nutrient deficiencies, especially in suboptimal soil conditions. This study aimed to analyse foliar fertiliser formulation research directions and their application in maize production. A literature search was conducted in the Web of Science (WoS) database. Bibliometric analyses were performed using the VOSviewer software (version 1.6.17). The changes in the publication trends of documents were tested using the Mann–Kendall test. The production effects of foliar fertilisation were independently synthesised. The results showed a strong positive increase in publication trends regarding maize foliar fertilisation (R2 = 0.7842). The predominant nutrients that affected maize production were nitrogen, phosphorous, potassium, zinc, iron, and manganese. The timely foliar application of nutrients corrected deficiencies and/or sustained nutrient supply under several abiotic stresses. Foliar application at critical growth stages like flowering and grain filling boosted carbohydrate and protein content, lipid levels, kernel size, mineral content, and the weight of the maize grain. This review identified important research gaps, namely genotype-specific responses, interactions with other agronomic practices, and long-term environmental effects. Full article
(This article belongs to the Special Issue Foliar Fertilization: Novel Approaches and Field Practices)
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<p>PRISMA showing literature search and screening process.</p>
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<p>Research publication trend analysis between 2014 and 2024.</p>
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<p>Total linkage of all-author keywords depicting predominant investigations of foliar fertiliser application in maize production.</p>
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<p>Total linkage of specific author keywords depicting predominant investigations of foliar fertiliser application in maize production.</p>
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<p>Total linkage of KeyWords Plus depicting predominant investigations of foliar fertiliser application in maize production.</p>
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17 pages, 23515 KiB  
Article
Hydro-Climatic Trends in Central Italy: A Case Study from the Aterno-Pescara River Watershed
by Mohsin Tariq, Eleonora Aruffo, Piero Chiacchiaretta and Piero Di Carlo
Sustainability 2025, 17(2), 493; https://doi.org/10.3390/su17020493 - 10 Jan 2025
Viewed by 444
Abstract
Climate change is reshaping water systems and trends in hydro-climatic variables, such as temperature, precipitation, and river runoff, providing critical insights into the hydrological shifts influenced by climate change. However, the impact of climate variability on these variables varies by geographic location, making [...] Read more.
Climate change is reshaping water systems and trends in hydro-climatic variables, such as temperature, precipitation, and river runoff, providing critical insights into the hydrological shifts influenced by climate change. However, the impact of climate variability on these variables varies by geographic location, making it necessary to study hydro-climatic variations in the Mediterranean’s changing climate to determine its impacts. This study analyzed the hydro-climatic trends in the Aterno-Pescara River watershed in central Italy from 1936 to 2013. We employed linear regression, Mann–Kendall, Sen’s slope, and Spearman correlation tests to estimate annual and seasonal trends. The results showed a significant warming trend on annual (0.037 °C/year) and seasonal time scales. Precipitation trends exhibited significant reductions annually, specifically during the autumn season, with a decrease of −0.68 mm/year; while showing a decline, other seasons were statistically insignificant. River runoff revealed drying trends annually and seasonally, decreasing by −0.29 m3 s−1/year over the study period. Furthermore, linear regression and Spearman correlation coefficients suggested a significant relationship between hydro-climatic variables with varying strengths (at 95% and 99% confidence levels) annually and seasonally. This decrease in precipitation and river runoff trends with the continuous rate points towards potential meteorological and hydrological droughts occurring in the future in this watershed. This study’s findings provide scientific grounds that could help develop sustainable strategies in the watershed. Full article
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<p>The map shows the Aterno-Pescara River watershed, the location of installed measuring stations, and other rivers in the Abruzzo region, adapted from [<a href="#B30-sustainability-17-00493" class="html-bibr">30</a>].</p>
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<p>Station-wise annual mean temperatures (1936–2013) show variations among various stations. The legend reports the station code; see <a href="#sustainability-17-00493-t002" class="html-table">Table 2</a> and <a href="#sustainability-17-00493-f001" class="html-fig">Figure 1</a> for the location.</p>
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<p>Station-wise total annual precipitation (1936–2013) shows variations among various stations. The legend reports the same information as <a href="#sustainability-17-00493-f002" class="html-fig">Figure 2</a>.</p>
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<p>The linear regression comparison plot of AMP and AMT (1936–2013) shows an increase in AMT and a decrease in AMP.</p>
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<p>The linear regression comparison plot of AMR and AMT (1936–2013) shows a decrease in AMR and an increase in AMT.</p>
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<p>The linear regression comparison plot of AMP and AMR (1936–2013) shows a decrease in AMR and AMP.</p>
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<p>The linear regression comparison plot of SMP and SMT (1936–2013) shows an increase in SMT and a decrease in SMP.</p>
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<p>The linear regression comparison plot of SMR and SMT (1936–2013) shows a decrease in SMR and an increase in SMT.</p>
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<p>The linear regression comparison plot of SMP and SMR (1936–2013) shows decreases in SMP and SMR.</p>
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<p>Comparison of SMT, SMP, and SMR with annual linear slopes. SMT indicates an increase, and SMP and SMR show a decrease in seasons and on an annual scale.</p>
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20 pages, 1106 KiB  
Article
Balancing Performance and Health in Elite Hungarian Athletes: The Relationship Among Disordered Eating Risk, Body Composition, and Nutrition Knowledge
by Réka Erika Kovács, Merve Alpay, István Karsai, Gusztáv József Tornóczky, Andrea Petróczi and Szilvia Boros
Nutrients 2025, 17(2), 231; https://doi.org/10.3390/nu17020231 - 9 Jan 2025
Viewed by 669
Abstract
Background: disordered eating (DE) and eating disorders (ED) can negatively impact athletes’ health, wellbeing, and athletic performance. Objective: this cross-sectional study aims to assess DE risk, body composition, and nutrition knowledge among elite Hungarian athletes. Methods: DE risk was assessed using DESA-6H and [...] Read more.
Background: disordered eating (DE) and eating disorders (ED) can negatively impact athletes’ health, wellbeing, and athletic performance. Objective: this cross-sectional study aims to assess DE risk, body composition, and nutrition knowledge among elite Hungarian athletes. Methods: DE risk was assessed using DESA-6H and EAT-26 scales, nutrition knowledge through the Abridged Nutrition for Sport Knowledge Questionnaire (A-NSKQ), and body composition with the OMRON BF511 device. The data were analyzed using Kendall’s tau correlations, Mann–Whitney U tests, and ROC analysis. Results: a total of 71 athletes participated (39.4% males, mean age = 24.8 years, SD = 4.8 years and 60.6% females, mean age = 24.3 years, SD = 4.3 years). At-risk scores on the DESA-6H scale were recorded for nine athletes (12.7%), while 32.4% scored in the risk zone on the EAT-26, with female athletes in aesthetic, endurance and weight-dependent sports being most affected. Low BF was observed in four males and four females. Nutrition knowledge (49.1%) was below the acceptable threshold. DESA-6H significantly correlated with EAT-26 scores, BMI, sports nutrition knowledge, and A-NSKQ total scores. A statistically significant difference by gender was found in the EAT-26 total score (p = 0.019, d = 0.65). Risk groups significantly differed in A-NSKQ scores (p = 0.026, d = 0.511) and sport nutrition knowledge, specifically (p = 0.016, d = 0.491). Using EAT-26 to identify at-risk athletes and the DESA-6H recommended cut-off, the ROC analysis showed a sensitivity of 29.1% and a specificity of 95.7%. Conclusions: insufficient nutrition knowledge plays a role in being at-risk for DE and ED. These results underscore the need for early detection, early sport nutrition education across all elite athletes, with particular attention to female athletes in aesthetic, endurance and weight-dependent sports, and for monitoring these athletes to prevent DE. Further work is warranted to optimize screening tools such as EAT-26 and DESA-6H for elite athletes. Full article
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<p>Athletes classified under the risk group from different sport disciplines based on DESA-6H and EAT-26 scores (<span class="html-italic">n</span> = 71).</p>
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<p>General and sports nutrition knowledge results.</p>
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<p>Overview of the athletes’ at-risk status of disordered eating, body composition, and nutrition knowledge. <span class="html-italic">n</span> = number of participants, SD = standard deviation, GENNUT: A-NSKQ general nutrition knowledge, SPORTNUT = A-NSKQ sport nutrition knowledge, ANSKQ S = A-NSKQ total score, BMI = body mass index, PBF = percent body fat.</p>
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<p>ROC curve analysis of the DESA-6H.</p>
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16 pages, 4228 KiB  
Article
Spatial and Temporal Variability of Extreme Hydroclimatic Events in the Bani River Basin
by Fousseini Kouyaté, François Kossi Guédjé, Assane Ndiaye and Orou Moctar Ganni Mampo
Hydrology 2025, 12(1), 5; https://doi.org/10.3390/hydrology12010005 - 5 Jan 2025
Viewed by 495
Abstract
Severe hydroclimatic events affect ecosystems and human livelihoods, creating significant challenges for managing water resources. This study analyzed the rainfall and river flow trends in the Bani River Basin (BRB) from 1991 to 2020. Using indices such as the maximum rainfall over a [...] Read more.
Severe hydroclimatic events affect ecosystems and human livelihoods, creating significant challenges for managing water resources. This study analyzed the rainfall and river flow trends in the Bani River Basin (BRB) from 1991 to 2020. Using indices such as the maximum rainfall over a one-day period (RX1DAY), maximum rainfall over a five-day period (RX5DAY), rainfall exceeding the 95th percentile (R95P), simple daily precipitation intensity (SDII), and peak discharge (Qmax), the modified Mann–Kendall test and Pettitt’s test were applied to assess the trends and identify potential breakpoints. The results revealed spatial variability, with southern regions showing reduced rainfall, while northeastern areas exhibit increasing extreme rainfall and river flow. The RX5DAY declined significantly after 2000, reflecting reductions in prolonged rainfall events, followed by the RX1DAY, which declined significantly after 2012, indicating a reduction in short-duration extremes. In contrast, the R99P, SDII, and Qmax exhibited positive trends, indicating intensifying rainfall intensity and extremes in discharge. A notable breakpoint was detected in 1993, marking a transition to increased extreme flows. The highest values of the rainfall indices (R95P, R99P, RX1DAY, RX5DAY, SDII) were concentrated in the southern part of the basin, while the north recorded lower values. These results highlight the basin’s vulnerability to climate variability and provide insights into hydroclimatic changes, serving as a basis for informed decision-making and future research. Full article
(This article belongs to the Section Statistical Hydrology)
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<p>Location of the Bani River Basin.</p>
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<p>Flowchart illustrating the methodology applied.</p>
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<p>Monthly rainfall comparison between CHIRPS data and observed station measurements in the BRB (2011–2019): (<b>a</b>) Segou, (<b>b</b>) San, (<b>c</b>) Bougouni and (<b>d</b>) Dioila.</p>
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<p>Spatial distribution of extreme rainfall indices across the study area (1991–2020): (<b>a</b>) maximum one-day precipitation, (<b>b</b>) maximum five-day precipitation, (<b>c</b>) very wet day, (<b>d</b>) extremely wet day, and (<b>e</b>) simple daily precipitation.</p>
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<p>Sen’s slope and trends for the BRB from 1991 to 2020: (<b>a</b>) RX1DAY, (<b>b</b>) RX5DAY, (<b>c</b>) R95P, (<b>d</b>) R99P, and (<b>e</b>) SDII. Black dots indicate statistically significant trends (<span class="html-italic">p</span> &lt; 0.05), showing the spatial patterns of changes in extreme rainfall indices across the basin.</p>
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<p>Breakpoint results for extreme precipitation over the BRB: (<b>a</b>) RX1DAY, (<b>b</b>) RX5DAY, (<b>c</b>) R95P, (<b>d</b>) R99P and (<b>e</b>) SDII.</p>
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<p>Standardized flow index over the BRB (1991–2020).</p>
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<p>Breakpoint results for the extreme flows over the BRB (1991–2020): (<b>a</b>) Qmax, (<b>b</b>) Q99P and (<b>c</b>) Q95P.</p>
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35 pages, 17133 KiB  
Article
Analysis of Climate Change Effects on Precipitation and Temperature Trends in Spain
by Blanca Arellano, Qianhui Zheng and Josep Roca
Land 2025, 14(1), 85; https://doi.org/10.3390/land14010085 - 3 Jan 2025
Viewed by 3157
Abstract
The objective of this study was to analyze the climate change experienced in Spain between 1971 and 2022 and to estimate the future climate (2050). The main objectives were as follows: (1) to analyze the temporal evolution of temperature from 1971 to the [...] Read more.
The objective of this study was to analyze the climate change experienced in Spain between 1971 and 2022 and to estimate the future climate (2050). The main objectives were as follows: (1) to analyze the temporal evolution of temperature from 1971 to the present, to quantify the warming process experienced in the case study and to evaluate the increase in extreme heat events (heatwaves); (2) to study the evolution of the precipitation regime to determine whether there is a statistically representative trend towards a drier climate and an increase in extreme precipitation; (3) to investigate the interaction between annual precipitation and the continuous increase in temperature; and (4) to estimate the future climate scenario for mainland Spain and the Balearic Islands towards 2050, analyzing the trends in land aridity and predicting a possible change from a Mediterranean climate to a warm steppe climate, according to the Köppen classification. The aim of this study was to test the hypothesis that the increase in temperature resulting from the global warming process implies a tendency towards progressive drought. Given the extreme annual variability of the climate, in addition to the ordinary least squares methodology, the techniques mainly used in this study were the Mann–Kendall test and the Kendall–Theil–Sen (KTS) regression. The Mann–Kendall test confirmed the very high statistical significance of the relationship between precipitation (RR) and maximum temperature (TX). If the warming trend experienced in recent years (1971–2022) continues, it is foreseeable that, by 2050, there will be a reduction in precipitation in Spain of between 14% and 23% with respect to the precipitation of the reference period (understood as the average between 1971 and 2000). Spain’s climate is likely to change from Mediterranean to warm steppe in the Köppen classification system (from “C” to “B”). Full article
(This article belongs to the Section Land–Climate Interactions)
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<p>Study area. Source: ESRI. Own elaboration.</p>
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<p>0.25° cells derived from E-OBS.</p>
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<p>Methodological framework.</p>
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<p>Evolution of maximum (TX) and minimum temperatures (TN) between 1971 and 2022.</p>
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<p>Spatial distribution of the increases in mean temperature (TG), maximum temperature (TX), and minimum temperature (TN) across Spain (1971–2022).</p>
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<p>Variation in summer days (SU) and tropical nights (TR) between 1971 and 2022. Note: the legend shows the variation (positive or negative) in summer days or tropical nights between 1971 and 2022.</p>
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<p>Heat thresholds (1971–2000). Note: The figure on the left shows the thresholds (day heat threshold, DHT) to identify days of extreme daytime heat. The figure on the right indicates the thresholds (night heat threshold, NHT) to identify nights of extreme heat.</p>
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<p>Number of daytime and nighttime heatwaves and duration of days, 1971–2022.</p>
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<p>Territory where daytime and nighttime heatwaves showed a tendency to increase between 1971 and 2022. Note: The images show, in blue, the territory where the OLS models indicate that daytime (DHWs, <b>left</b>) and nighttime (NHWs, <b>right</b>) heatwaves tended to increase in the period 1971–2022. The white stripes show the area in which the regression coefficient is statistically representative at 95% confidence.</p>
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<p>Annual rainfall (RR) and annual precipitation &lt;= 10 mm/day (RR10mm) (1971–2022).</p>
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<p>Temporal trend (1971–2022) of annual rainfall and &lt;10 mm/day. Note: The figure shows, for the 839 OLS models, the sign of the regression coefficients between annual rainfall (RR) and &lt;10 mm/day (RR10mm) as dependent variables, and the year as an independent variable. The image above in the left shows the territory in which the OLS models indicated a reduction in rainfall (blue color) between 1971 and 2022. The image above in the right shows the degree of statistical significance (<span class="html-italic">p</span>-value) of the models. In the bottom left is the Spanish territory (blue color) where the total annual rainfall below 10 mm/day has decreased. In the bottom right is the degree of statistical significance of the OLS models.</p>
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<p>Dry days and consecutive days with precipitation of less than 1 mm/day (1971–2022).</p>
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<p>Temporal trend (1971–2022) of dry days and consecutive days with a precipitation of &lt;1 mm. Note: The figure shows, for the 839 OLS models, the sign of the regression coefficients between dry days (DDs) and consecutive days with precipitation &lt;1 mm/day (CDRR1mm) as dependent variables, and the year as an independent variable. The image above in the left shows the territory in which the OLS models indicated an increase in number of DDs (orange color) between 1971 and 2022. The image above in the right shows the degree of statistical significance (<span class="html-italic">p</span>-value) of the models. In the bottom left is the Spanish territory (orange color) where the consecutive number of days with precipitation less than 1 mm has increased. In the bottom right is the degree of statistical significance of the OLS models.</p>
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<p>Five-day precipitation amount (RRX5days), extreme wet days (RR30mm), and torrential precipitation (RR60mm) (1971–2022).</p>
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<p>Extreme and torrential precipitation (1971–2022). Note: The upper part of the figure shows the cumulative annual precipitation on days with rainfall equal to or greater than 30 mm (RR30mm) and the lower part shows the cumulative annual precipitation on days with rainfall equal to or greater than 60 mm (RR60mm). On the left, the trend towards an increase (in dark blue) or decrease (in light blue) in extreme precipitation is shown, and, on the right, the statistical significance of the OLS models is given.</p>
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<p>Annual rainfall and annual precipitation &lt;=10 mm/day vs. maximum temperature (TX).</p>
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<p>Annual rainfall and annual precipitation &lt;= 10 mm/day vs. maximum temperature (839 models).</p>
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<p>Annual precipitation &gt;= 30 mm/day vs. minimum temperature (TN).</p>
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<p>Annual precipitation &gt;= 30 mm/day vs. minimum temperature (839 models).</p>
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<p>Köppen climate classification. 1971–2000, 1991–2020, and 2041–2060.</p>
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24 pages, 106853 KiB  
Article
Assessment of Vegetation Dynamics in Xinjiang Using NDVI Data and Machine Learning Models from 2000 to 2023
by Nan Ma, Shanshan Cao, Tao Bai, Zhihao Yang, Zhaozhao Cai and Wei Sun
Sustainability 2025, 17(1), 306; https://doi.org/10.3390/su17010306 - 3 Jan 2025
Viewed by 545
Abstract
This study utilizes NASA’s Normalized Difference Vegetation Index (NDVI) data from the Google Earth Engine (GEE) platform and employs methods such as mean analysis, trend analysis, and the Hurst index to assess NDVI dynamics in Xinjiang, with a particular focus on desert, meadow, [...] Read more.
This study utilizes NASA’s Normalized Difference Vegetation Index (NDVI) data from the Google Earth Engine (GEE) platform and employs methods such as mean analysis, trend analysis, and the Hurst index to assess NDVI dynamics in Xinjiang, with a particular focus on desert, meadow, and grassland vegetation. Furthermore, multiple linear regression, random forest, support vector machines, and XGBoost models are applied to construct and evaluate the NDVI prediction models. The key driving forces are identified and ranked based on the results of the optimal model. Changes in the vegetation cover in response to these driving forces are analyzed using the Mann–Kendall test and partial correlation analysis. The results indicate the following: (1) From 2000 to 2023, the annual variation in NDVI in Xinjian fluctuates at a rate of 0.0012 per year. The intra-annual trend follows an inverted U shape, with meadow vegetation exhibiting the highest monthly NDVI fluctuations. (2) During this period, the annual average NDVI in Xinjiang ranges from 0 to 0.3, covering 74.74% of the region. Spatially, higher NDVI values are observed in the north and northwest, while lower values are concentrated in the south and southeast. (3) The overall slope of the variation in NDVI in Xinjiang between 2000 and 2023 ranges between −0.034 and 0.047, indicating no significant upward trend. According to the Hurst index, future projections suggest a shift from vegetation improvement to potential degradation. (4) Machine learning models are developed to predict NDVI, with random forest and XGBoost showing the highest precision. Soil moisture, runoff, and potential evaporation are identified as key drivers. In the last 24 years, the temperatures in Xinjiang have generally increased, while precipitation, soil moisture, and runoff have declined. There is a significant negative correlation between NDVI and both temperature and potential evaporation, while the correlation between NDVI and precipitation, soil moisture, and runoff is positive and significant, with distinct spatial variations throughout the region. The overall trend of vegetation cover in Xinjiang has been increasing, but the future outlook is less promising. Enhanced environmental monitoring and protective measures are essential moving forward. Full article
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<p>Distribution of vegetation types of Xinjiang and area percentage charts.</p>
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<p>Overall flowchart of the research on NDVI changes and their drivers in Xinjiang.</p>
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<p>Interannual variation in NDVI during the growing season, 2000–2023.</p>
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<p>Intra-annual variation in monthly mean values of NDVI from 2000 to 2023.</p>
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<p>Distribution of annual mean values of NDVI for different vegetation types during the growing season from 2000 to 2023. (<b>a</b>) Xinjiang. (<b>b</b>) Desert vegetation. (<b>c</b>) Grassland vegetation. (<b>d</b>) Meadow vegetation.</p>
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<p>Distribution of slope and <span class="html-italic">p</span>-value for the growing season in Xinjiang from 2000 to 2023. (<b>a</b>) Slope. (<b>b</b>) <span class="html-italic">p</span>-value.</p>
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<p>Trend distribution of annual average values of NDVI during the growing season from 2000 to 2023. (<b>a</b>) Xinjiang. (<b>b</b>) Desert vegetation. (<b>c</b>) Grassland vegetation. (<b>d</b>) Meadow vegetation.</p>
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<p>Distribution of H for different vegetation types in Xinjiang from 2000 to 2023. (<b>a</b>) Xinjiang. (<b>b</b>) Desert vegetation. (<b>c</b>) Grassland vegetation. (<b>d</b>) Meadow vegetation.</p>
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<p>Future trends in vegetation cover in Xinjiang. (<b>a</b>) Xinjiang. (<b>b</b>) Desert vegetation. (<b>c</b>) Grassland vegetation. (<b>d</b>) Meadow vegetation.</p>
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<p>Future trends in area percentage of different vegetation types.</p>
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<p>Heat map of correlations between drivers.</p>
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<p>The importance of each influencing factor calculated by random forest and XGBoost. (<b>a</b>) Feature importance calculated by XGBoost. (<b>b</b>) Feature importance calculated by random forest.</p>
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<p>Trends in temperature, precipitation, soil moisture, runoff and potential evapotranspiration as a percentage of plot.</p>
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<p>Results of significance tests for partial correlation coefficients of air temperature, precipitation, soil moisture, runoff, and potential evaporation. (<b>a</b>) Potential evaporation. (<b>b</b>) Precipitation. (<b>c</b>) Runoff. (<b>d</b>) Soil moisture. (<b>e</b>) Temperature.</p>
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<p>Results of significance tests for air temperature, precipitation, soil moisture, runoff, and potential evaporation.</p>
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22 pages, 16143 KiB  
Article
Trends and Spatiotemporal Patterns of the Meteorological Drought in the Ili River Valley from 1961 to 2023: An SPEI-Based Study
by Su Hang, Alim Abbas, Bilal Imin, Nijat Kasim and Zinhar Zunun
Atmosphere 2025, 16(1), 43; https://doi.org/10.3390/atmos16010043 - 2 Jan 2025
Viewed by 283
Abstract
Drought presents significant challenges in arid regions, influencing local climate and environmental dynamics. While the large-scale climatic phenomena in Xinjiang, northwest China, are well-documented, the finer-scale climatic variability in subregions such as the Ili River Valley (IRV) remains insufficiently studied. This knowledge gap [...] Read more.
Drought presents significant challenges in arid regions, influencing local climate and environmental dynamics. While the large-scale climatic phenomena in Xinjiang, northwest China, are well-documented, the finer-scale climatic variability in subregions such as the Ili River Valley (IRV) remains insufficiently studied. This knowledge gap impedes effective regional planning and environmental management in this ecologically sensitive area. In this study, we analyze the spatiotemporal evolution of drought in the IRV from 1961 to 2023, using data from ten meteorological stations. The SPEI drought index, along with Sen’s trend analysis, the Mann–Kendall test, the cumulative departure method, and wavelet analysis, were employed to assess drought patterns. Results show a significant drying trend in the IRV, starting in 1995, with frequent drought events from 2018 onwards, and no notable transition year observed from wet to dry conditions. The overall drought rate was −0.09 per decade, indicating milder drought severity in the IRV compared to broader Xinjiang. Seasonally, the IRV experiences drier summers and wetter winters compared to regional averages, with negligible changes in autumn and milder drought conditions in spring. Abrupt changes in the drying seasons occurred later in the IRV than in Xinjiang, with delays of 21 years for summer, and over 17 and 35 years for spring and autumn, respectively, indicating a lagged response. Spatially, the western plains are more prone to aridification than the central and eastern mountainous regions. The study also reveals significant differences in drought cycles, which are longer than those in Xinjiang, with distinct wet–dry phases observed across multiple time scales and seasons, emphasizing the complexity of drought variability in the IRV. In conclusion, the valley exhibits unique drought characteristics, including milder intensity, pronounced seasonal variation, spatial heterogeneity, and notable resilience to climate change. These findings underscore the need for region-specific drought management strategies, as broader approaches may not be effective at the subregional scale. Full article
(This article belongs to the Section Meteorology)
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<p>Sketch map of the study area (the black line represents the country border, the green area indicates the Xinjiang Uyghur Autonomous Region of China, and the red area denotes the Ili River Valley).</p>
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<p>Fluctuation diagrams of SPEI-1 (<b>a</b>), SPEI-3 (<b>b</b>), and SPEI-12 (<b>c</b>) for the Ili River Valley region from 1961 to 2023 (The deeper the green, the more humid it is; the deeper the red, the more arid it becomes).</p>
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<p>Results of the Mann–Kendall (M-K) mutation test (<b>a</b>) and anomaly analysis (<b>b</b>).</p>
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<p>Temporal variations in SPEI in the Ili River Valley Region from 1961 to 2023.</p>
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<p>Changing characteristics of meteorological drought in the Ili River Valley from 1961 to 2023; spring (<b>a</b>), summer (<b>b</b>), autumn (<b>c</b>), and winter (<b>d</b>).</p>
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<p>Variation trends in seasonal SPEI interannual anomalies and cumulative anomalies in the Ili River Valley from 1961 to 2023; spring (<b>a</b>), summer (<b>b</b>), autumn (<b>c</b>), and winter (<b>d</b>).</p>
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<p>Spatial variation trends in seasonal SPEI in the Ili River Valley from 1961 to 2023; spring (<b>a</b>), summer (<b>b</b>), autumn (<b>c</b>), and winter (<b>d</b>).</p>
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<p>(<b>a</b>) Real contour map of the annual SPEI wavelet coefficients, (<b>b</b>) wavelet variance of the annual SPEI in the Ili River Valley from 1961 to 2023.</p>
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<p>(<b>a1</b>–<b>a4</b>) Real contour map of the seasonal SPEI wavelet coefficients, (<b>b1</b>–<b>b4</b>) wavelet variance of the seasonal SPEI in the Ili River Valley from 1961 to 2023; spring (<b>a1</b>,<b>b1</b>), summer (<b>a2</b>,<b>b2</b>), autumn (<b>a3</b>,<b>b3</b>), and winter (<b>a4</b>,<b>b4</b>).</p>
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<p>Three-dimensional scatter plot of the time scales and average periods of the SPEI on an annual scale at various stations in the Ili River Valley from 1961 to 2023.</p>
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<p>Three-dimensional scatter plot of the time scales and average periods of the SPEI on a seasonal scale at various stations in the Ili River Valley from 1961 to 2023; spring (<b>a</b>), summer (<b>b</b>), autumn (<b>c</b>), and winter (<b>d</b>).</p>
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16 pages, 1798 KiB  
Article
Evaluation of Evapotranspiration Prediction for Cassava Crop Using Artificial Neural Network Models and Empirical Models over Cross River Basin in Nigeria
by Oluwadamilare Oluwasegun Eludire, Oluwaseun Temitope Faloye, Michael Alatise, Ayodele Ebenezer Ajayi, Philip Oguntunde, Tayo Badmus, Abayomi Fashina, Oluwafemi E. Adeyeri, Idowu Ezekiel Olorunfemi and Akinwale T. Ogunrinde
Water 2025, 17(1), 87; https://doi.org/10.3390/w17010087 - 1 Jan 2025
Viewed by 897
Abstract
The accurate assessment of water availability throughout the cassava cropping season (the initial, developmental, mid-season, and late stages) is crucial for mitigating the impacts of climate change on crop production. Using the Mann–Kendall Test, we investigated the trends in rainfall and cassava crop [...] Read more.
The accurate assessment of water availability throughout the cassava cropping season (the initial, developmental, mid-season, and late stages) is crucial for mitigating the impacts of climate change on crop production. Using the Mann–Kendall Test, we investigated the trends in rainfall and cassava crop evapotranspiration (ETc) within the Cross River basin in Nigeria. Reference evapotranspiration (ETo) was based on two approaches, namely Artificial Neural Network (ANN) modelling and three established empirical models—the Penman–Monteith (considered the standard method), Blaney–Morin–Nigeria (BMN), and Hargreaves–Samani (HAG) models. ANN predictions were performed by using inputs from BMN and HAG parameters, denoted as BMN-ANN and HAG-ANN, respectively. The results from the ANN models were compared to those obtained from the Penman–Monteith method. Remotely sensed meteorological data spanning 39 years (1979–2017) were acquired from the Climatic Research Unit (CRU) to estimate ETc, while cassava yield data were acquired from the International Institute of Tropical Agriculture (IITA), Ibadan. The study revealed a significant upward trend in cassava crop ETc over the study period. Additionally, the ANN models outperformed the empirical models in terms of prediction accuracy. The BMN-ANN model with a Tansig activation function and a 3-3-1 architecture (number of input neurons, hidden layers, and output neurons) achieved the highest performance, with a coefficient of determination (R2) of 0.9890, a root mean square error (RMSE) of 0.000056 mm/day, and a Willmott’s index of agreement (d) of 0.9960. There is a decreasing trend in cassava yield in the region and further analysis indicated potential average daily water deficits of approximately −1.1 mm/day during the developmental stage. These deficits could potentially hinder root biomass, yield, and overall cassava yield in the Cross River basin. Our findings highlight the effectiveness of ANN modelling for irrigation planning, especially in the face of a worsening climate change scenario. Full article
(This article belongs to the Special Issue Crop Evapotranspiration, Crop Irrigation and Water Savings)
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<p>Map of Nigeria showing the Cross River basin, showing the 22 stations used by ArcGIS Pro 3.1.</p>
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<p>Network architecture showing input, hidden, and output layer connections.</p>
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<p>Annual trend in cassava cropping seasonal rainfall.</p>
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<p>Annual yield of cassava over Cross River basin from IITA yield data.</p>
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<p>Neural network structure of BMN-LogSig-ANN-3-1-1.</p>
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26 pages, 6030 KiB  
Article
Carbon Budget Assessment and Influencing Factors for Forest Enterprises in the Key State-Owned Forest Area of the Greater Khingan Range, Northeast China
by Hui Wang, Wenshu Lin, Jinzhuo Wu and Zhaoping Luan
Land 2025, 14(1), 56; https://doi.org/10.3390/land14010056 - 31 Dec 2024
Viewed by 403
Abstract
Analyzing the spatial and temporal changes in the carbon budget and its influencing factors is the basis for formulating effective measures to reduce emissions and increase sinks. This study establishes a carbon budget assessment model for forest enterprises, calculating forest carbon stocks and [...] Read more.
Analyzing the spatial and temporal changes in the carbon budget and its influencing factors is the basis for formulating effective measures to reduce emissions and increase sinks. This study establishes a carbon budget assessment model for forest enterprises, calculating forest carbon stocks and enterprise emissions using volume-derived biomass and emission factor methods. The spatiotemporal evolution characteristics of carbon budgets for forest enterprises in the key state-owned forest area (2017–2021) were analyzed using various methods, including the Mann-Kendall (MK) test and hotspot analysis. Influencing factors are identified through correlation analysis and the optimal parameter geographical detector (OPGD), while their spatial-temporal variations and causal relationships are analyzed using the geographical and temporal weighted regression model (GTWR) and structural equation modeling (SEM). The carbon budget in the Greater Khingan Range state-owned forest area averaged 10.16 × 106 t CO2-eq from 2017 to 2021, showing a gradual upward trend. The average annual carbon budget of forest enterprises was 1.02 × 106 t CO2-eq, which was highest in the central regions and lowest in the periphery. Soil pH, forest area, and elevation are the primary factors. The interaction between paired factors enhances the explanatory power of their impact, and the effects of different influencing factors exhibit both positive and negative variations across forest enterprises. In addition, the middle-aged forest tending area and average annual precipitation positively influenced forest area and soil pH, indirectly enhancing the carbon budget through multifactor interactions. This research can enhance the understanding of the carbon budget in forest enterprises, providing scientific support for the ecological protection of state-owned forests and contributing to the development of sustainable forestry practices that indirectly benefit societal well-being and economic resilience. Full article
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<p>Location of the Greater Khingan Mountains National Forest Area in China, with subregions highlighted as northern, central, and southern.</p>
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<p>Flowchart of the study.</p>
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<p>Spatial distribution of carbon budget for forest enterprises (2017–2021).</p>
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<p>Trends of carbon budgets (2017–2021): (<b>a</b>) overall trend, (<b>b</b>) northern region, (<b>c</b>) central region, and (<b>d</b>) southern region.</p>
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<p>Evolution characteristics of carbon budget based on the KDE: (<b>a</b>) overall, (<b>b</b>) northern region, (<b>c</b>) central region, and (<b>d</b>) southern region.</p>
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<p>(<b>a</b>) Gini coefficients, (<b>b</b>) Moran’s I, (<b>c</b>) Hotspots, and (<b>d</b>) LISA agglomeration maps of carbon budgets (2017–2021).</p>
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<p>Correlation coefficients and significance between carbon budget and different influencing factors (X<sub>i</sub> variables). Note: The definitions of the X<sub>i</sub> variables are provided in the paragraph above.</p>
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<p>OPGD results for carbon budget analysis: (<b>a</b>) factor detection, (<b>b</b>) interaction detection, and (<b>c</b>) ecological detection of significant influencing factors.</p>
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<p>Spatial distribution of regression coefficients for GTWR model.</p>
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<p>Results of SEM model. (<b>a</b>) Pathway diagram of the relationships between significant influencing factors and the carbon budget. (<b>b</b>) Statistics of standardized total effect. Red arrows indicate negative correlation, and green arrows indicate negative correlation. The line weight corresponds to the strength of the correlation. The numbers on the arrows are standardized path coefficients, and asterisks indicate statistical significance (*** <span class="html-italic">p</span> &lt; 0.001; ** <span class="html-italic">p</span>&lt; 0.01; * <span class="html-italic">p</span> &lt; 0.05).</p>
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21 pages, 10301 KiB  
Article
Integrated Approach to Understanding Perceived Importance and Changes in Watershed Ecosystem Services (WESs): Insights from Central Nepal
by Nabin Dhungana, Chun-Hung Lee, Samjhana Adhikari, Bishal Kumar Rayamajhi, Udit Chandra Aryal and Pramod Ghimire
Sustainability 2025, 17(1), 62; https://doi.org/10.3390/su17010062 - 26 Dec 2024
Viewed by 715
Abstract
With environmental changes, sustaining watershed ecosystem services requires understanding community perceptions and preferences. Integrated approaches considering community perceptions, climate change, and land use cover change are crucial. We address a study gap by combining climate change and land use cover change data with [...] Read more.
With environmental changes, sustaining watershed ecosystem services requires understanding community perceptions and preferences. Integrated approaches considering community perceptions, climate change, and land use cover change are crucial. We address a study gap by combining climate change and land use cover change data with an analysis of community perceptions to evaluate the watershed ecosystem services situation in Nepal’s Khageri Khola Watershed. Data from in-depth stakeholder interviews (n = 16), household perception surveys (n = 440), and participant observations (n = 5) were supplemented by meteorological and land use cover change data. Descriptive analysis, index value calculation, Spearman’s Rho correlation, and chi-square statistics were used to understand linkages between socio-demographics, climate change perceptions, watershed ecosystem services importance, and changes in watershed ecosystem services supply. The Mann–Kendall test, Sen’s slope calculation, and land use cover change analysis considered temperature, precipitation, and land use. Among watershed ecosystem services, communities prioritized drinking water as the most important and biodiversity support as the least important. Watershed ecosystem services exhibited decreasing trends, with soil fertility and productivity notably high (89%) and natural hazard control low (41%). Significant alignment existed between community perceptions and local climate indicators, unlike the incongruity found with land use cover changes, especially regarding water bodies. Socio-demographic factors influenced community perceptions. Policy recommendations include analyzing watershed-level community demand and preferences, integrating community perceptions with climate change and land use cover change data in decision making, engaging communities, equitable sharing of the benefits generated by watershed ecosystem services, and considering socio-demographic and topographic diversity in tailoring management strategies. Full article
(This article belongs to the Special Issue Advances in Ecosystem Services and Urban Sustainability, 2nd Edition)
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<p>Study watershed in Chitwan District, Central Nepal, showing watershed boundaries, rivers, irrigation canals, forest corridors, buffer zone, local government areas, and land use. Note: OWL represent other wooded land.</p>
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<p>Methodological framework for identifying key WESs, importance, and trends for management and policy inputs.</p>
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<p>Stacked bar chart showing the rank index values of WESs across socio-demographic groups, with higher values indicating greater importance. The figure idea is adopted from [<a href="#B22-sustainability-17-00062" class="html-bibr">22</a>].</p>
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<p>Respondents’ perceptions of local climate change indicators.</p>
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<p>Bar chart showing total annual precipitation (in mm), and trend line showing mean temperature (in °C) at stations near the watershed from 1980 to 2023, along with Sen’s slope equation.</p>
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<p>Respondents’ perceptions of WES supply trends over the past decade.</p>
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<p>Percentage change in watershed land use/land cover per category from 2000 to 2019.</p>
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<p>Map showing watershed land use/land cover changes (gain or loss) across seven categories from 2000 to 2019.</p>
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<p>Watershed land use maps from 2000 (<b>a</b>) and 2019 (<b>b</b>).</p>
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24 pages, 4808 KiB  
Article
Climate Variability and Adaptation Strategies in a Pastoralist Area of the Eastern Bale Zone: The Case of Sawena District, Ethiopia
by Mesfin Bekele Gebbisa and Zsuzsanna Bacsi
Appl. Sci. 2025, 15(1), 69; https://doi.org/10.3390/app15010069 - 25 Dec 2024
Viewed by 441
Abstract
This study was conducted in Sawena district, located in the Eastern Bale Zone of Ethiopia, with the aim of analyzing climate variability and identifying adaptation strategies. Secondary data covering the period from 1984 to 2023 were utilized, along with structured and unstructured questionnaires. [...] Read more.
This study was conducted in Sawena district, located in the Eastern Bale Zone of Ethiopia, with the aim of analyzing climate variability and identifying adaptation strategies. Secondary data covering the period from 1984 to 2023 were utilized, along with structured and unstructured questionnaires. Primary data were gathered from 350 pastoralist households across six kebeles through a household survey. This study used the Mann–Kendall test, Sen’s slope estimator, the coefficient of variation, descriptive statistics, and a multivariate probit model to analyze climate variability and adaptation strategies. The Mann–Kendall test, Sen’s slope estimator, and coefficient of variation analysis results showed significant rainfall increases in September, October, and November, with high winter variability and an upward autumn trend. Temperature analysis revealed consistent warming, with the greatest increases in September (0.049 °C/year) and summer (0.038 °C/year), and an annual mean rise of 0.034 °C per year, indicating climate shifts affecting pastoralist and agro-pastoral livelihood strategies and water resources that lead the area toward vulnerability. The descriptive results indicated that pastoralist households have adopted various adaptation strategies: 45.1% participate in seasonal livestock migration, 26.3% rely on productive safety net programs, 19% pursue livelihood diversification, and 9.7% engage in agroforestry. Multivariate analysis indicates that education, age, credit access, livestock ownership, asset value, and media exposure influence these strategies. The findings highlight the importance of policies to enhance climate resilience through diversification, sustainable land management, and improved access to resources like credit and markets, alongside strengthened education and targeted extension services. Full article
(This article belongs to the Special Issue Potential Impacts and Risks of Climate Change on Agriculture)
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<p>Map of the study area. Source: authors’ own construction.</p>
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<p>Trend of winter season rainfall.</p>
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<p>Trend of spring season rainfall.</p>
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<p>Trend of Summer season rainfall.</p>
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<p>Trend of autumn season rainfall.</p>
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<p>Trend of annual rainfall in Sawena district.</p>
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<p>Trend of winter season temperature.</p>
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<p>Trend of mean annual temperature.</p>
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<p>The most common adaptation and coping strategies of households in Sawena district. Source: authors’ own computation.</p>
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17 pages, 2272 KiB  
Article
Attribution Identification of Runoff Changes Based on the Budyko Elasticity Coefficient Method: A Case Study of the Middle and Upper Reaches of the Jinghe River in the Yellow River Basin
by Xueliang Wang, Haolin Li, Weidong Huang, Lemin Wei, Junfeng Liu and Rensheng Chen
Atmosphere 2025, 16(1), 6; https://doi.org/10.3390/atmos16010006 - 25 Dec 2024
Viewed by 276
Abstract
The impacts of climate change and human activities on water resources are a complex and integrated process and a key factor for effective water resource management in semi-arid regions, especially in relation to the Jinghe River basin (JRB), a major tributary of the [...] Read more.
The impacts of climate change and human activities on water resources are a complex and integrated process and a key factor for effective water resource management in semi-arid regions, especially in relation to the Jinghe River basin (JRB), a major tributary of the Yellow River basin. The Sen’s slope estimator and the Mann–Kendall test (M–K test) are implemented to examine the spatial and temporal trends of the hydrological factors, while the elasticity coefficient method based on Budyko’s theory of hydrothermal coupling is employed to quantify the degree of runoff response to the various influencing factors, from 1971 to 2020. The results reveal that the runoff at Pingliang (PL), Jingchuan (JC), and Yangjiaping (YJP) hydrological stations shows an obvious and gradual decreasing trend during the study period, with a sudden change in about 1986, while precipitation shows a fluctuating and increasing trend alongside a potential evapotranspiration-induced fluctuating and decreasing trend. Compared to the previous period, a change of −29%, in relative terms, in the runoff at the YJP hydrological station is observed. The interaction of human activities and climate change in the watershed contributes to the sharp decrease in runoff, with precipitation, potential evapotranspiration, and human activities accounting for −14.3%, −15.1%, and 70.6% of the causes of the change in runoff, respectively. Human activities (e.g., construction of water conservancy projects), precipitation, and potential evapotranspiration are the main factors contributing to the change in runoff. Full article
(This article belongs to the Special Issue The Hydrologic Cycle in a Changing Climate)
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<p>Distribution of hydrological and meteorological stations in the study area.</p>
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<p>Steps used to process and analyze data, i.e., our research framework.</p>
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<p>Trends of <math display="inline"><semantics> <mrow> <mi>Q</mi> </mrow> </semantics></math> (runoff depth), <math display="inline"><semantics> <mrow> <mi>P</mi> </mrow> </semantics></math> (precipitation), <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>E</mi> <mi>T</mi> </mrow> <mrow> <mn>0</mn> </mrow> </msub> </mrow> </semantics></math> (potential evapotranspiration), and <math display="inline"><semantics> <mrow> <mi>R</mi> <mi>C</mi> </mrow> </semantics></math> (runoff coefficient) at three hydrological stations in the upper and middle reaches of the Jinghe River. (<b>a</b>–<b>c</b>) <math display="inline"><semantics> <mrow> <mi>Q</mi> </mrow> </semantics></math> (runoff depth), (<b>d</b>–<b>f</b>) <math display="inline"><semantics> <mrow> <mi>P</mi> </mrow> </semantics></math> (precipitation), (<b>g</b>–<b>i</b>) <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>E</mi> <mi>T</mi> </mrow> <mrow> <mn>0</mn> </mrow> </msub> </mrow> </semantics></math> (potential evapotranspiration), and (<b>j</b>–<b>l</b>) <math display="inline"><semantics> <mrow> <mi>R</mi> <mi>C</mi> </mrow> </semantics></math> (runoff coefficient). PL, JC and YJP denote the Pingliang, Jingchuan, and Yangjiaping hydrological stations, respectively.</p>
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<p>Trends in the interannual variability of the elasticity coefficients of (<b>a</b>–<b>c</b>) precipitation <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>ε</mi> </mrow> <mrow> <mi>P</mi> </mrow> </msub> </mrow> </semantics></math>, (<b>d</b>–<b>f</b>) potential evapotranspiration <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>ε</mi> </mrow> <mrow> <msub> <mrow> <mi>E</mi> <mi>T</mi> </mrow> <mrow> <mn>0</mn> </mrow> </msub> </mrow> </msub> </mrow> </semantics></math>, and (<b>g</b>–<b>i</b>) surface condition <math display="inline"><semantics> <mrow> <msub> <mrow> <mi>ε</mi> </mrow> <mrow> <mi>n</mi> </mrow> </msub> </mrow> </semantics></math>. PL, JC, and YJP denote the Pingliang, Jingchuan, and Yangjiaping hydrological stations, respectively.</p>
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<p>Volume and contribution of each element to runoff changes at three hydrological stations in the middle (<b>b</b>,<b>c</b>,<b>e</b>,<b>f</b>) and upper (<b>a</b>,<b>d</b>) reaches of the Jinghe River, 1971–2020. PL, JC, and YJP denote the Pingliang, Jingchuan, and Yangjiaping hydrological stations, respectively.</p>
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<p>Relationship between the parameter <span class="html-italic">n</span> and the vegetation cover NDVI at the YJP hydrological station in the middle and upper reaches of the Jinghe River from 1986 to 2020. (<b>a</b>) Trend plot of surface parameter n; (<b>b</b>) Trend plot of NDVI; (<b>c</b>) Scatter plot of surface parameter n fitted to NDVI.</p>
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20 pages, 5002 KiB  
Article
Impact of Changes in Rainfall and Temperature on Production of Darjeeling Tea in India
by Netrananda Sahu, Rajiv Nayan, Arpita Panda, Ayush Varun, Ravi Kesharwani, Pritiranjan Das, Anil Kumar, Suraj Kumar Mallick, Martand Mani Mishra, Atul Saini, Sumat Prakash Aggarwal and Sridhara Nayak
Atmosphere 2025, 16(1), 1; https://doi.org/10.3390/atmos16010001 - 24 Dec 2024
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Abstract
Globally, there has been a lot of focus on climate variability, especially variability in annual precipitation and temperatures. Depending on the area, different climate variables have different degrees of variation. Therefore, analyzing the temporal and spatial changes or dynamics of meteorological or climatic [...] Read more.
Globally, there has been a lot of focus on climate variability, especially variability in annual precipitation and temperatures. Depending on the area, different climate variables have different degrees of variation. Therefore, analyzing the temporal and spatial changes or dynamics of meteorological or climatic variables in light of climate change is crucial to identifying the changes induced by climate and providing workable adaptation solutions. This study examined how climate variability affects tea production in Darjeeling, West Bengal, India. It also looked at trends in temperature and rainfall between 1991 and 2023. In order to identify significant trends in these climatic factors and their relationship to tea productivity, the study used a variety of statistical tests, including the Sen’s Slope Estimator test, the Mann–Kendall’s test, and regression tests. The study revealed a positive growth trend in rainfall (Sen’s slope = 0.25, p = 0.001, R2 = 0.032), maximum temperature (Sen’s slope = 1.02, p = 0.026, R2 = 0.095), and minimum temperature (Sen’s slope = 4.38, p = 0.006, R2 = 0.556). Even with the rise in rainfall, there has been a decline in tea productivity, as seen by the sharp decline in both the tea cultivated area and the production of tea. The results obtained from the regression analysis showed an inverse relationship between temperature anomalies and tea yield (R = −0.45, p = 0.02, R2 = 0.49), indicating that the growing temperatures were not favorable for the production of tea. Rainfall anomalies, on the other hand, positively correlated with tea yield (R = 0.56, p = 0.01, R2 = 0.68), demonstrating that fluctuations in rainfall have the potential to affect production but not enough to offset the detrimental effects of rising temperatures. These results underline how susceptible the tea sector in Darjeeling is to climate change adversities and the necessity of adopting adaptive methods to lessen these negative consequences. The results carry significance not only for regional stakeholders but also for the global tea industry, which encounters comparable obstacles in other areas. Full article
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Figure 1
<p>Location of the study area. The red dot in the map represents the geographical locations of the 87 tea gardens of the Darjeeling area.</p>
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<p>Trend in rainfall from 1991 to 2023.</p>
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<p>Trend in maximum temperature from 1991 to 2023.</p>
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<p>Trend in minimum temperature from 1991 to 2023.</p>
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<p>Box and whisker plot showing monthly rainfall (1991 to 2023).</p>
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<p>Box and whisker plot showing monthly maximum temperature (1991 to 2023).</p>
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<p>Box and whisker plot for monthly minimum temperature (1991 to 2023).</p>
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<p>Trend analysis of tea production under linear, logarithmic, and exponential growth.</p>
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<p>Trend in tea production area (linear, logarithmic, and exponential growth).</p>
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<p>Relationship between climatic parameter anomalies and yield anomalies.</p>
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