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20 pages, 7652 KiB  
Article
Potential Impacts of Land Use Change on Ecosystem Service Supply and Demand Under Different Scenarios in the Gansu Section of the Yellow River Basin, China
by Yingchen Bai, Conghai Han, Fangying Tang, Zuzheng Li, Huixia Tian, Zhihao Huang, Li Ma, Xuefan Hu, Jianchao Wang, Bo Chen, Lixiang Sun, Xiaoqin Cheng and Hairong Han
Remote Sens. 2025, 17(3), 489; https://doi.org/10.3390/rs17030489 - 30 Jan 2025
Viewed by 339
Abstract
The degradation of ecosystem services (ES) poses a significant obstacle to regional sustainable development. Land-use change is widely recognized as a pivotal factor driving the spatio-temporal dynamics of ES supply and demand. However, the future impact of land-use changes on supply–demand risks remains [...] Read more.
The degradation of ecosystem services (ES) poses a significant obstacle to regional sustainable development. Land-use change is widely recognized as a pivotal factor driving the spatio-temporal dynamics of ES supply and demand. However, the future impact of land-use changes on supply–demand risks remains largely unknown. To fill this knowledge gap, we conducted a study in the Gansu section of the Yellow River Basin. By integrating Cellular Automata (CA) and an enhanced Markov model within the GeoSOS-FLUS framework, we dynamically simulated land-use changes under three scenarios—the Normal Development Scenario (NDS), Ecological Protection Scenario (EPS), and Rapid Socio-economic Development Scenario (RDS)—spanning from 2020 to 2050. Furthermore, we employed the InVEST model to analyze the spatio-temporal pattern of supply, demand, supply-to-demand ratios, and supply–demand risks for water provision, carbon storage, and soil conservation under all scenarios. Firstly, all scenarios project an increase in built-up land, primarily from unused land, shrubland, grassland, and cropland. Forest land and water bodies remain stable. Secondly, water provision increases, but demand grows faster, leading to supply–demand imbalances, with high-risk areas in the north, central, and east. Soil conservation shows balanced supply and demand with high-risk areas in the north. Carbon storage remains stable, with high-risk areas in the central and east regions. Thirdly, high-risk areas for water provision increase under all scenarios, particularly under the Rapid Socio-economic Development scenario. Full article
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Figure 1
<p>Location map of the Gansu section of the Yellow River Basin.</p>
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<p>The framework of LUCC modeling and supply–demand risk evaluation.</p>
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<p>The principle of FLUS model operation.</p>
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<p>Comparison between observations and the FLUS simulation in 2010 and 2020.</p>
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<p>Spatial patterns of land use in Gansu Section of the Yellow River Basin during 2030–2050 under three scenarios.</p>
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<p>Land-use transfer map from 2020 to 2030, 2020 to 2040, and 2020 to 2050 under three scenarios.</p>
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<p>The supply–demand risk of water yield in Gansu Section of the Yellow River Basin during 2020–2030, 2020–2040, and 2020–2050 under NDS, EPS, and RDS scenarios, respectively.</p>
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<p>The supply–demand risk of carbon storage in Gansu Section of the Yellow River Basin during 2020–2030, 2020–2040, and 2020–2050 under NDS, EPS, and RDS scenarios, respectively.</p>
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<p>The supply–demand risk of soil conservation in Gansu Section of the Yellow River Basin during 2020–2030, 2020–2040, and 2020–2050 under NDS, EPS, and RDS scenarios, respectively.</p>
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25 pages, 30317 KiB  
Article
Multi-Scenario Prediction of Dynamic Responses of the Carbon Sink Potential in Land Use/Land Cover Change in Areas with Steep Slopes
by Wanli Wang, Zhen Zhang, Yangyang Wang, Jing Ding, Guolong Li, Heling Sun and Chao Deng
Appl. Sci. 2025, 15(3), 1319; https://doi.org/10.3390/app15031319 - 27 Jan 2025
Viewed by 487
Abstract
Terrestrial ecosystems are vital carbon sinks that can effectively restrain the rise in CO2 in the atmosphere. How ecosystem carbon storage (CS) in semi-arid watershed areas with slow urbanization is affected by comprehensive factors of the environment and land use, along with [...] Read more.
Terrestrial ecosystems are vital carbon sinks that can effectively restrain the rise in CO2 in the atmosphere. How ecosystem carbon storage (CS) in semi-arid watershed areas with slow urbanization is affected by comprehensive factors of the environment and land use, along with its temporal and spatial changes has still not been fully explored. Notably, there is a paucity of research on the temporal and spatial changes and development trends of CS in the rapid deformation belt of slopes from the eastern margin of the Qinghai–Tibet Plateau to the Loess Plateau. Taking Bailong River Basin (BRB) as an example, this study combined GeoSOS-FLUS, the InVEST model, and localized “social–economic–nature” scenario to simulate the long-term dynamic evolution of CS. The aim was to study how topographic factors and land use change, and their interactions impact carbon sinks and gradient effects in steep-slope areas, and then find out the relationship between carbon sinks and topographic factors to explore strategies to improve regional carbon sink capacity. The results showed that the following: (1) CS in BRB increased year by year, with a total increase of 558 tons (3.19%), and showed significant spatial heterogeneity, mainly due to the conversion of woodland and arable land; (2) except for land use type, the relationship between CS and topographic gradient is inverted U-shaped, showing a complex spatial response; and (3) it is estimated that by 2050, under the arable land protection and natural development scenarios, CS will decrease by 0.07% and 0.005%, respectively, encroachment on undeveloped mountain areas, while the ecological protection scenario gives priority to protecting the carbon sinks of woodland and grassland, and CS will increase by 0.37%. This study supports the implementation of targeted ecological protection measures through topographic gradient zoning, provides a reference for policy makers in similar topographic regions to effectively manage the spatial heterogeneity of CS, and helps further strengthen global and regional climate change mitigation efforts. Full article
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Figure 1
<p>BRB location map.</p>
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<p>Spatial distribution of the driving factors affecting land use and CS.</p>
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<p>Research design framework.</p>
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<p>Spatial and area changes of land use in BRB from 2000 to 2020 (<b>a</b>–<b>c</b>).</p>
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<p>Spatial and temporal distribution of CS in BRB, (<b>a</b>) is CS in 2000, (<b>b</b>) is CS in 2010, and (<b>c</b>) is CS in 2020.</p>
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<p>Characteristics of CS changes at different stages of BRB, (<b>a</b>) is the CS space change from 2000 to 2010, (<b>b</b>) is the CS space change from 2010 to 2020, and (<b>c</b>) is the CS space change from 2000 to 2020.</p>
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<p>Terrain feature map of BRB.</p>
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<p>Distribution characteristics of CS at different topographic gradients in BRB.</p>
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<p>Bivariate LISA cluster map of CS and topographic gradient drivers.</p>
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<p>Changes in CS in the BRB under three scenarios: change trend for total CS under arable land protection scenario from 2000 to 2050 (<b>a</b>), change trend for total CS in 2000–2050 in an ecological protection scenario (<b>b</b>), change trend for total CS in 2000–2050 in a natural development scenario (<b>c</b>), and comparison of total CS in three different scenarios (<b>d</b>).</p>
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<p>Spatial distribution of CS in the BRB in three scenarios. ALP-2030 (<b>a</b>), ALP-2040 (<b>b</b>), ALP-2050 (<b>c</b>), EP-2030 (<b>d</b>), EP-2040 (<b>e</b>), EP-2050 (<b>f</b>), ND-2030 (<b>g</b>), ND-2040 (<b>h</b>), ND-2030 (<b>i</b>). (<b>A</b>–<b>C</b>) represent local locations and enlarged contrast plots.</p>
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<p>The natural terrain gradient effect was used for regional zoning.</p>
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27 pages, 5657 KiB  
Article
Identification and Prediction of Land Use Spatial Conflicts in Urban Agglomeration on the Northern Slope of Tianshan Mountains Under the Background of Urbanization
by Yunfei Ma, Yusuyunjiang Mamitimin and Ailijiang Nuerla
Land 2025, 14(2), 228; https://doi.org/10.3390/land14020228 - 22 Jan 2025
Viewed by 349
Abstract
In past decades, urbanization has entered a phase of rapid development, resulting in an intensified utilization of land resources. The finite nature of these resources has led to increased pressure on land availability, giving rise to a phenomenon known as land use conflict. [...] Read more.
In past decades, urbanization has entered a phase of rapid development, resulting in an intensified utilization of land resources. The finite nature of these resources has led to increased pressure on land availability, giving rise to a phenomenon known as land use conflict. This conflict is particularly evident in the frequent conversion of land categories, with urban impervious surfaces increasingly encroaching upon forests, grasslands, and agricultural land. Such encroachments trigger a series of land use conflict issues, which subsequently impact the function and structure of regional ecosystems. This paper analyzes the spatial and temporal changes in land use and land cover (LULC) within the urban agglomeration on the northern slope of Tianshan Mountain. It measures and evaluates the spatial and temporal evolution of land use conflicts in the study area from 1990 to 2020, utilizing conflict-related theories and the landscape risk evaluation model. Additionally, the paper explores the spatial and temporal dimensions of land use conflicts under three scenarios—natural development (ND), cultivation priority (CP), and ecological priority (EP)—for the years 2030 and 2050, informed by the Future Land Use Simulation (FLUS) model. The results indicate that unused land constitutes the predominant land use type, accounting for over 50% of the total area. The areas of cultivated land, water bodies, and urban land are experiencing an increasing trend, while the areas of forestland, grassland, and unused land are witnessing a decreasing trend. The level of land use spatial conflicts during the study period showed a decreasing and then increasing trend, with an overall upward trend and an increase in the average value of 0.03. In terms of the proportion of spatial units, mild and general conflicts exhibited a decreasing trend, with reductions of 4.21% and 2.95%, respectively. Conversely, the proportion of medium conflicts increased significantly, rising by 7.33%, while severe conflicts experienced a slight increase of 0.23%. Under the ND, CP, and EP scenarios, the spatial and temporal dynamics of future land use conflicts varied. However, the study area was predominantly characterized by general conflicts in both 2030 and 2050. In 2030, the proportions of spatial units experiencing general conflicts in the three scenarios are projected to be 61.20%, 60.39%, and 57.51%, respectively. In comparison, these proportions are projected to be 59.24%, 62.70%, and 56.29% in 2050, respectively. The anticipated future changes in land use spatial conflicts vary across different scenarios. Notably, the ND scenario indicates a rising conflict level in the study area over the next 30 years, with an overall increase of 0.03 in the mean value. In contrast, the changes in the index under the CP and EP scenarios are relatively stable. Full article
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Figure 1
<p>Geographical location (<b>a</b>) and topographic map (<b>b</b>) of the study area.</p>
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<p>Drivers of land use, including DEM (<b>a</b>), slope (<b>b</b>), slope direction (<b>c</b>), average annual temperature (<b>d</b>), annual rainfall (<b>e</b>), NDVI (<b>f</b>), distance to rural areas (<b>g</b>), distance to towns (<b>h</b>), distance to roads (<b>i</b>), distance to railroads (<b>j</b>), distance to highways (<b>k</b>), GDP (<b>l</b>), and population (<b>m</b>).</p>
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<p>Spatial distribution of LULC in 1990 (<b>a</b>), 2000 (<b>b</b>), 2010 (<b>c</b>), and 2020 (<b>d</b>).</p>
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<p>Spatial distribution of predicted LULC in 2030 under ND (<b>a</b>), CP (<b>b</b>), and EP (<b>c</b>), and in 2050 under ND (<b>d</b>), CP (<b>e</b>), and EP (<b>f</b>).</p>
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<p>Spatial distribution of the LUCI in 1990 (<b>a</b>), 2000 (<b>b</b>), 2010 (<b>c</b>), and 2020 (<b>d</b>).</p>
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<p>Moran scatterplot of the LUCI in 1990 (<b>a</b>), 2000 (<b>b</b>), 2010 (<b>c</b>), and 2020 (<b>d</b>).</p>
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<p>Localized significance maps of spatial land use conflicts in 1990 (<b>a</b>), 2000 (<b>b</b>), 2010 (<b>c</b>), and 2020 (<b>d</b>).</p>
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<p>Local autocorrelation Lisa clustering of spatial land use conflicts in 1990 (<b>a</b>), 2000 (<b>b</b>), 2010 (<b>c</b>), and 2020 (<b>d</b>).</p>
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<p>Spatial distribution of predicted LUCI in 2030 under ND (<b>a</b>), CP (<b>b</b>), and EP (<b>c</b>), and in 2050 under ND (<b>d</b>), CP (<b>e</b>), and EP (<b>f</b>).</p>
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24 pages, 3442 KiB  
Article
Phenomenological Modeling of Antibody Response from Vaccine Strain Composition
by Victor Ovchinnikov and Martin Karplus
Antibodies 2025, 14(1), 6; https://doi.org/10.3390/antib14010006 - 16 Jan 2025
Viewed by 450
Abstract
The elicitation of broadly neutralizing antibodies (bnAbs) is a major goal of vaccine design for highly mutable pathogens, such as influenza, HIV, and coronavirus. Although many rational vaccine design strategies for eliciting bnAbs have been devised, their efficacies need to be evaluated in [...] Read more.
The elicitation of broadly neutralizing antibodies (bnAbs) is a major goal of vaccine design for highly mutable pathogens, such as influenza, HIV, and coronavirus. Although many rational vaccine design strategies for eliciting bnAbs have been devised, their efficacies need to be evaluated in preclinical animal models and in clinical trials. To improve outcomes for such vaccines, it would be useful to develop methods that can predict vaccine efficacies against arbitrary pathogen variants. As a step in this direction, here, we describe a simple biologically motivated model of antibody reactivity elicited by nanoparticle-based vaccines using only antigen amino acid sequences, parametrized with a small sample of experimental antibody binding data from influenza or SARS-CoV-2 nanoparticle vaccinations. Results: The model is able to recapitulate the experimental data to within experimental uncertainty, is relatively insensitive to the choice of the parametrization/training set, and provides qualitative predictions about the antigenic epitopes exploited by the vaccine, which are testable by experiment. For the mosaic nanoparticle vaccines considered here, model results suggest indirectly that the sera obtained from vaccinated mice contain bnAbs, rather than simply different strain-specific Abs. Although the present model was motivated by nanoparticle vaccines, we also apply it to a mutlivalent mRNA flu vaccination study, and demonstrate good recapitulation of experimental results. This suggests that the model formalism is, in principle, sufficiently flexible to accommodate different vaccination strategies. Finally, we show how the model could be used to rank the efficacies of vaccines with different antigen compositions. Conclusions: Overall, this study suggests that simple models of vaccine efficacy parametrized with modest amounts of experimental data could be used to compare the effectiveness of designed vaccines. Full article
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Graphical abstract

Graphical abstract
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<p>Illustration of the amino acid encoding procedure [<a href="#B31-antibodies-14-00006" class="html-bibr">31</a>]. (<b>A</b>): Multiple alignment <math display="inline"><semantics> <mover accent="true"> <mi mathvariant="bold-italic">S</mi> <mo>^</mo> </mover> </semantics></math> of <math display="inline"><semantics> <msub> <mi>N</mi> <mi>s</mi> </msub> </semantics></math> sequences, each having <math display="inline"><semantics> <msub> <mi>N</mi> <mi>r</mi> </msub> </semantics></math> residues, including gaps, with <math display="inline"><semantics> <mrow> <msub> <mi>s</mi> <mrow> <mi>i</mi> <mi>j</mi> </mrow> </msub> <mrow> <mo>∈</mo> <mo>{</mo> <mi>A</mi> <mo>,</mo> <mi>C</mi> <mo>,</mo> <mi>D</mi> <mo>,</mo> <mi>E</mi> <mo>,</mo> <mi>F</mi> <mo>,</mo> <mi>G</mi> <mo>,</mo> <mi>H</mi> <mo>,</mo> <mi>I</mi> <mo>,</mo> <mi>K</mi> <mo>,</mo> <mi>L</mi> <mo>,</mo> <mi>M</mi> <mo>,</mo> <mi>N</mi> <mo>,</mo> </mrow> </mrow> </semantics></math><math display="inline"><semantics> <mrow> <mi>P</mi> <mo>,</mo> <mi>Q</mi> <mo>,</mo> <mi>R</mi> <mo>,</mo> <mi>S</mi> <mo>,</mo> <mi>T</mi> <mo>,</mo> <mi>V</mi> <mo>,</mo> <mi>W</mi> <mo>,</mo> <mi>Y</mi> <msup> <mo>,</mo> <mo>′</mo> </msup> <msup> <mo>−</mo> <mo>′</mo> </msup> <mrow> <mo>}</mo> </mrow> </mrow> </semantics></math>. (<b>B</b>): Embedded alignment <math display="inline"><semantics> <mover accent="true"> <mi mathvariant="bold-italic">X</mi> <mo>^</mo> </mover> </semantics></math>; each residue type in <math display="inline"><semantics> <mover accent="true"> <mi mathvariant="bold-italic">S</mi> <mo>^</mo> </mover> </semantics></math> shown in A is associated with a 3-dimensional real-valued vector <math display="inline"><semantics> <msub> <mi mathvariant="bold">x</mi> <mrow> <mi>i</mi> <mi>j</mi> </mrow> </msub> </semantics></math>=<math display="inline"><semantics> <mrow> <mo>{</mo> <msubsup> <mi>x</mi> <mrow> <mi>i</mi> <mi>j</mi> </mrow> <mn>1</mn> </msubsup> <mo>,</mo> <msubsup> <mi>x</mi> <mrow> <mi>i</mi> <mi>j</mi> </mrow> <mn>2</mn> </msubsup> <mo>,</mo> <msubsup> <mi>x</mi> <mrow> <mi>i</mi> <mi>j</mi> </mrow> <mn>3</mn> </msubsup> <mo>}</mo> </mrow> </semantics></math>, which is interpreted as Cartesian coordinates of the residue.</p>
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<p>Parameter optimization (<math display="inline"><semantics> <mi>α</mi> </semantics></math>,<math display="inline"><semantics> <mi>β</mi> </semantics></math>) in the strain similarity function Equation (<a href="#FD4-antibodies-14-00006" class="html-disp-formula">4</a>) applied to influenza data [<a href="#B20-antibodies-14-00006" class="html-bibr">20</a>] using a diffusion constant <span class="html-italic">D</span> = 0.4. (<b>A</b>): A 2D scan of the (<math display="inline"><semantics> <mi>α</mi> </semantics></math>,<math display="inline"><semantics> <mi>β</mi> </semantics></math>) landscape; the white line corresponds to a cubic spline curve through the minimum values of the mean squared error (MSE) over the range of <math display="inline"><semantics> <mi>α</mi> </semantics></math> at each <math display="inline"><semantics> <mi>β</mi> </semantics></math>; (<b>B</b>): MSE corresponding to the white line in A plotted in 1D for several values of the diffusion constant <span class="html-italic">D</span>.</p>
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<p>Illustration of the nanoparticles used in the vaccinations modeled here [<a href="#B20-antibodies-14-00006" class="html-bibr">20</a>,<a href="#B21-antibodies-14-00006" class="html-bibr">21</a>]. The nanoparticles are drawn in black, and the antigens are in color, with different colors indicating different strains. (<b>A</b>): Nanoparticles corresponding to the mosaic vaccines V1, V2, V4, and V8 in <a href="#antibodies-14-00006-t002" class="html-table">Table 2</a>. (<b>B</b>): Mosaic vaccine (top) vs. nanoparticle mixture vaccine (bottom). (<b>C</b>): Hypothetical elicitation of strain-specific Abs (blue Ab binding to blue antigens) vs. cross-reactive bnAbs (purple Ab binding to blue and red antigens) by the mosaic vaccine via different Fabs.</p>
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<p>Comparison of model results with the experimental IgG titers for influenza [<a href="#B20-antibodies-14-00006" class="html-bibr">20</a>]. (<b>A</b>,<b>B</b>): best fit to experiment; in (<b>A</b>), the colors correspond to experimental data for vaccines in <a href="#antibodies-14-00006-t002" class="html-table">Table 2</a> (red <span style="color:red">■</span> V1, green <span style="color:#00FF00">■</span> V2, orange <span style="color:orange">■</span> V4, blue <span style="color:blue">■</span> V8), and the black outer bars are model values. The black unfilled circles and squares correspond to model titers computed after setting to zero the residue weights in the HA stem and HA head, respectively (see text). (<b>C</b>): Comparison of 252 possible fits in which 5 strains were used for fitting (training) and 5 for testing (red <span style="color:red">∘</span>: <math display="inline"><semantics> <msub> <mi>C</mi> <mi>P</mi> </msub> </semantics></math>, green <span style="color:#00FF00">▿</span>: <math display="inline"><semantics> <msub> <mi>C</mi> <mi>S</mi> </msub> </semantics></math>). (<b>D</b>): Influenza hemagglutinin (PDB ID: 3LZG [<a href="#B39-antibodies-14-00006" class="html-bibr">39</a>]) monomer colored by model weights using the color map blue-gray-red (corresponding to low-medium-high).</p>
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<p>Comparison of Model 1 results with the experimental IgG titers for coronavirus [<a href="#B21-antibodies-14-00006" class="html-bibr">21</a>]. (<b>A</b>,<b>B</b>): Best fit to experiment; in (<b>A</b>), the colors correspond to experimental data for vaccines in <a href="#antibodies-14-00006-t003" class="html-table">Table 3</a> (red <span style="color:red">■</span> V1, green <span style="color:#00FF00">■</span> V4A, orange <span style="color:orange">■</span> V4B, blue <span style="color:blue">■</span> V8), and the black outer bars are model values. (<b>C</b>): Comparison of 126 possible fits in which 5 strains were used for fitting (training) and 4 for testing (red <span style="color:red">∘</span>: <math display="inline"><semantics> <msub> <mi>C</mi> <mi>P</mi> </msub> </semantics></math>, green <span style="color:#00FF00">▿</span>: <math display="inline"><semantics> <msub> <mi>C</mi> <mi>S</mi> </msub> </semantics></math>, blue <span style="color:blue">×</span>: <math display="inline"><semantics> <msub> <mi>C</mi> <mi>P</mi> </msub> </semantics></math> for training sets that include SARS-2). (<b>D</b>): SARS-CoV-2 receptor binding domain (RBD), colored by model weights using the color map blue-gray-red (corresponding to low-medium-high); PDB ID: 6VXX [<a href="#B41-antibodies-14-00006" class="html-bibr">41</a>].</p>
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<p>Comparison of model results with the experimental IgG titers for mRNA influenza vaccination [<a href="#B44-antibodies-14-00006" class="html-bibr">44</a>]. (<b>A</b>,<b>B</b>): Best fit to experiment; in (<b>A</b>), the subplot title indicates the vaccine, the titers are shown for the same 20 antigens (see <a href="#app1-antibodies-14-00006" class="html-app">Table S1</a>). The experimental titers are shown with error bars in blue, and the model results are shown as red circles. The vertical dashed lines separate HA group 1, HA group 2, and HB antigens (going from left to right); in (<b>B</b>), red circles, green triangles, and blue squares correspond to 20-HA, H1, and H3 vaccinations, and to the panels in A (left to right). (<b>C</b>): Comparison of 1000 training/testing splits in which 10 strains were randomly chosen for fitting (training) and the remaining 10 for testing (red <span style="color:red">∘</span>: <math display="inline"><semantics> <msub> <mi>C</mi> <mi>P</mi> </msub> </semantics></math>, green <span style="color:#00FF00">▿</span>: <math display="inline"><semantics> <msub> <mi>C</mi> <mi>S</mi> </msub> </semantics></math>). (<b>D</b>): Influenza hemagglutinin (PDB ID: 3LZG [<a href="#B39-antibodies-14-00006" class="html-bibr">39</a>]) monomer colored by model weights using the color map blue-gray-red (corresponding to low-medium-high).</p>
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<p>Two–dimensional projections of influenza hemagglutinin sequences onto principal components. Colors: projections of avian, swine, and human influenza type A spike protein sequences spanning the years 1918–2019 and subtypes 1–18, which were downloaded from the NIH influenza research database [<a href="#B38-antibodies-14-00006" class="html-bibr">38</a>]; the sequences were clustered to 97% identity. Principal component analysis (PCA) was performed in MATLAB [<a href="#B35-antibodies-14-00006" class="html-bibr">35</a>], as described in <span class="html-italic">Methods</span>; black bullets: projections of 11 antigens with solved Xray crystal structures (labeled with PDB codes). The strains corresponding to the PDB IDs and their sequence accession numbers are listed in <a href="#app1-antibodies-14-00006" class="html-app">Table S2</a>.</p>
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<p>Comparison of predicted IgG titers for four hypothetical np vaccines using data of Cohen et al. [<a href="#B20-antibodies-14-00006" class="html-bibr">20</a>]. <span class="html-italic">Cocktail</span> refers to the mixture of 11 HA antigens, as given in <a href="#app1-antibodies-14-00006" class="html-app">Table S2</a>.</p>
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22 pages, 5237 KiB  
Article
From Policy to Practice: Assessing Carbon Storage in Fujian Province Using Patch-Generating Land Use Simulation and Integrated Valuation of Ecosystem Services and Tradeoffs Models
by Qin Nie, Wang Man, Zongmei Li and Xuewen Wu
Land 2025, 14(1), 179; https://doi.org/10.3390/land14010179 - 16 Jan 2025
Viewed by 407
Abstract
Simulating and predicting carbon storage under different development scenarios is crucial for formulating effective carbon management strategies and achieving carbon neutrality goals. However, studies that focus on specific regions and incorporate local policy context require further investigation. Taking Fujian Province as a case [...] Read more.
Simulating and predicting carbon storage under different development scenarios is crucial for formulating effective carbon management strategies and achieving carbon neutrality goals. However, studies that focus on specific regions and incorporate local policy context require further investigation. Taking Fujian Province as a case study, this research developed four policy-driven scenarios—natural development, farmland protection, urban development, and ecological protection—based on local policy frameworks. Using the PLUS (Patch-generating Land Use Simulation) and InVEST (Integrated Valuation of Ecosystem Services and Tradeoffs) models, the study simulated and predicted the carbon storage dynamics under each scenario. The results show that carbon storage declined from 1995 to 2020, mainly due to the conversion of forests and agricultural land into construction areas. The ecological protection scenario demonstrated the highest potential for carbon storage recovery, projecting an increase to 2.02 billion tons by 2030, driven by afforestation and conservation initiatives. Conversely, the urban development scenario posed the greatest risks, leading to substantial losses. Key conservation areas, including 12 priority districts, were identified in the western and northwestern regions, while coastal urban areas, comprising 31 vulnerable districts, face significant carbon storage losses. These findings emphasize the need for balanced land use policies that prioritize both urban development and ecological protection to achieve sustainable carbon management. Full article
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Figure 1
<p>Land use distribution in Fujian from 1995 to 2020. Note: 1~6 indicates cultivated land, forest land, grassland, water, construction land, and unused land, respectively.</p>
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<p>Spatial distribution of carbon storage in Fujian in 2020.</p>
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<p>Land use of various forecast scenarios in Fujian Province by 2030.</p>
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<p>Spatial pattern of carbon storage under various scenarios in Fujian Province in 2030.</p>
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<p>Key protection areas and vulnerable regions in the spatial distribution of carbon storage.</p>
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21 pages, 9620 KiB  
Article
Impacts of Future Climate Change and Xiamen’s Territorial Spatial Planning on Carbon Storage and Sequestration
by Wei Zhu, Ting Lan and Lina Tang
Remote Sens. 2025, 17(2), 273; https://doi.org/10.3390/rs17020273 - 14 Jan 2025
Viewed by 461
Abstract
The intensification of climate change and the implementation of territorial spatial planning policies have jointly increased the complexity of future carbon storage changes. However, the impact of territorial spatial planning on carbon storage under future climate change remains unclear. Therefore, this study aims [...] Read more.
The intensification of climate change and the implementation of territorial spatial planning policies have jointly increased the complexity of future carbon storage changes. However, the impact of territorial spatial planning on carbon storage under future climate change remains unclear. Therefore, this study aims to reveal the potential impacts of future climate change and territorial spatial planning on carbon storage and sequestration, providing decision support for addressing climate change and optimizing territorial spatial planning. We employed the FLUS model, the InVEST model, and the variance partitioning analysis (VPA) method to simulate carbon storage under 15 different scenarios that combine climate change scenarios and territorial spatial planning for Xiamen in 2035, and to quantify the individual and combined impacts of territorial spatial planning and climate change on ecosystem carbon sequestration. The results showed that (1) by 2035, Xiamen’s carbon storage capacity is expected to range from 32.66 × 106 Mg to 33.00 × 106 Mg under various scenarios, reflecting a decrease from 2020 levels; (2) the implementation of territorial spatial planning is conducive to preserving Xiamen’s carbon storage, with the urban development boundary proving to be the most effective; (3) carbon storage is greatly affected by climate change, with RCP 4.5 more effective than RCP 8.5 in maintaining higher levels of carbon storage; and (4) the influence of territorial spatial planning on carbon sequestration consistently exceeds that of climate change, particularly under high-emission scenarios, where the regulatory effect of planning is especially significant. Full article
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<p>Study area. (<b>a</b>) Location of Xiamen, China. (<b>b</b>) Land use in Xiamen in 2020. Source: created by the authors, based on Landsat 8 OLI/TIRS dataset (<a href="https://www.gscloud.cn/" target="_blank">https://www.gscloud.cn/</a> (accessed on 6 July 2024)).</p>
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<p>The process of land use change simulation in the FLUS model.</p>
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<p>Land use map of Xiamen in 2035 across 15 scenarios.</p>
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<p>The area change rate of various land use types across various scenarios (compared with 2020).</p>
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<p>Spatial patterns of carbon storage in Xiamen in 2035 across various scenarios.</p>
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<p>The amount of carbon storage in Xiamen across various scenarios.</p>
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<p>Carbon sequestration for each subdistrict (or township) in different scenarios in Xiamen.</p>
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<p>Hot/cold spots of carbon sequestration for each subdistrict (or township) in different scenarios in Xiamen.</p>
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<p>Variance partitioning Venn diagram. The diagram illustrates the unique and intersecting contributions of climate and territorial spatial planning to carbon sequestration. The intersection represents the percentage of variance explained by shared explanatory variables, with no value area indicating that the shared variance is zero or negative. Residuals represent the percentage of unexplained variance.</p>
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15 pages, 4433 KiB  
Article
Data from Emergency Medical Service Activities: A Novel Approach to Monitoring COVID-19 and Other Infectious Diseases
by Daniele del Re, Luigi Palla, Paolo Meridiani, Livia Soffi, Michele Tancredi Loiudice, Martina Antinozzi and Maria Sofia Cattaruzza
Diagnostics 2025, 15(2), 181; https://doi.org/10.3390/diagnostics15020181 - 14 Jan 2025
Viewed by 493
Abstract
Background: Italy, particularly the northern region of Lombardy, has experienced very high rates of COVID-19 cases and deaths. Several indicators, i.e., the number of new positive cases, deaths and hospitalizations, have been used to monitor virus spread, but all suffer from biases. [...] Read more.
Background: Italy, particularly the northern region of Lombardy, has experienced very high rates of COVID-19 cases and deaths. Several indicators, i.e., the number of new positive cases, deaths and hospitalizations, have been used to monitor virus spread, but all suffer from biases. The aim of this study was to evaluate an alternative data source from Emergency Medical Service (EMS) activities for COVID-19 monitoring. Methods: Calls to the emergency number (112) in Lombardy (years 2015–2022) were studied and their overlap with the COVID-19 pandemic, influenza and official mortality peaks were evaluated. Modeling it as a counting process, a specific cause contribution (i.e., COVID-19 symptoms, the “signal”) was identified and enucleated from all other contributions (the “background”), and the latter was subtracted from the total observed number of calls using statistical methods for excess event estimation. Results: A total of 6,094,502 records were analyzed and filtered for respiratory and cardiological symptoms to identify potential COVID-19 patients, yielding 742,852 relevant records. Results show that EMS data mirrored the time series of cases or deaths in Lombardy, with good agreement also being found with seasonal flu outbreaks. Conclusions: This novel approach, combined with a machine learning predictive approach, could be a powerful public health tool to signal the start of disease outbreaks and monitor the spread of infectious diseases. Full article
(This article belongs to the Special Issue Advances in Disease Prediction)
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<p>Number of calls per day (weekly averaged) for respiratory and cardiologic issues as a function of time for the different SOREU areas in Lombardy.</p>
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<p><b>Top</b>: Number of calls per day for respiratory and cardiologic issues as a function of time. In green and overlaid, with the baseline contribution being fitted with the parameterization described in the text. <b>Bottom</b>: The same as above, but with the subtraction of the fitted baseline contribution.</p>
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<p>Number of calls per day (weekly averaged) for respiratory and cardiologic issues as a function of time and subtracted from the fitted baseline contribution compared with the official number of positive COVID-19 cases in Lombardy (red line).</p>
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<p><b>Top</b>: Number of deaths per day for Lombardy from ISTAT. Overlaid, baseline contribution fitted with the parameterization described in the text. <b>Bottom</b>: Comparison of the baseline-subtracted distributions of the number of calls for respiratory and cardiologic issues per week from AREU and the number of deaths from ISTAT.</p>
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<p><b>Top</b>: Comparison of the baseline-subtracted distributions of the age of the patients for (<b>left</b>) the three COVID-19 waves and (<b>right</b>) flu for different years. <b>Bottom</b>: Comparison of the baseline-subtracted distributions for COVID- 19 (period 3), flu (period 2) and baseline (period 1).</p>
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<p>Comparison of the baseline-subtracted distributions of the patients for COVID-19 (period 3), flu (period 2) and baseline (period 1). The top right shows sex (0 = female, 1 = male, 2 = undefined), while the top left shows the hour of the day of the call. The middle left shows the severity of the call (triage coding at the site of rescue: 0 = white, 1 = green, 2 = green/yellow, 3 = yellow, 4 = red), the middle right shows the code of the call (triage coding in hospital: 0 = white, 1 = green, 2 = yellow, 3 = red, 4 = black). The bottom left shows the time passed between the ambulance leaving the hospital and its arrival to the patient location, and the bottom right shows the time passed between the ambulance arrival to the patient location and its arrival to hospital.</p>
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26 pages, 8101 KiB  
Article
Synergistic Enhancement of Carbon Sinks and Connectivity: Restoration and Renewal of Ecological Networks in Nanjing, China
by Renfei Zhang, Hongye Li and Zhicheng Liu
Land 2025, 14(1), 93; https://doi.org/10.3390/land14010093 - 5 Jan 2025
Viewed by 554
Abstract
Urbanization has led to a reduction in green space, weakening the region’s carbon sink capacity and stability and bringing a series of ecological problems, making the restoration and improvement of the ecological environment crucial. This study used Nanjing, China, as a case to [...] Read more.
Urbanization has led to a reduction in green space, weakening the region’s carbon sink capacity and stability and bringing a series of ecological problems, making the restoration and improvement of the ecological environment crucial. This study used Nanjing, China, as a case to construct an ecological network by applying Morphological Spatial Pattern Analysis (MSPA) and the Linkage Mapper (LM) tool based on circuit theory. The connectivity of ecological patches was evaluated by calculating the delta potential connectivity index (dPC). The CASA model (Carnegie–Ames–Stanford approach) was applied to quantify carbon sequestration in Nanjing. We propose an innovative carbon sink index (CSI) that integrates three indicators: capacity, efficiency, and variability. This index assesses the carbon sink function of ecological patches from both static and dynamic perspectives. Using the Future Land Use Simulation (FLUS) model, we simulated carbon sequestration changes in 2035, providing insights for risk assessment and future optimization strategies. The results reveal a significant positive correlation between node connectivity and both carbon sink capacity and efficiency, indicating that enhancing connectivity at key nodes can effectively improve its carbon sequestration. On this basis, by coupling dPC and CSI indices to classify ecological network nodes, we proposed four strategies for optimization: ecological conservation, structural connectivity, carbon sink improvement, and synergistic enhancement. Finally, by adding 26 ecological stepping stones, 32 ecological corridors, and optimizing landscape components, we achieved dual improvements in both the structural and functional aspects of the ecological network. After optimization, the network connectivity increased by 1.6% and the carbon sink increased by 3.82%, demonstrating a significant improvement. This study emphasizes that by protecting, enhancing, and restoring ecological spaces, the carbon sequestration function and stability of urban ecological networks can be effectively improved. These findings provide valuable insights for the scientific management of ecological spaces in urbanized areas. Full article
(This article belongs to the Special Issue Planning for Sustainable Urban and Land Development)
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<p>Geographic location analysis of Nanjing, China. (<b>a</b>) Geographic location of Yangtze River Delta in China; (<b>b</b>) Geographic location of Nanjing in the Yangtze River Delta; (<b>c</b>) Land use of Nanjing in 2020.</p>
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<p>Framework diagram of ecological network optimization research in Nanjing city.</p>
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<p>Optimization strategies for ecological networks in Nanjing.</p>
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<p>Construction of the ecological network in Nanjing. (<b>a</b>) Ecological sources of Nanjing in 2000, 2010, and 2020; (<b>b</b>) Resistance surfaces of Nanjing in 2000, 2010, and 2020; (<b>c</b>) Ecological network of Nanjing in 2000, 2010, and 2020.</p>
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<p>Spatial distribution of dPC index for ecological sources of Nanjing in 2020.</p>
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<p>Land use and ecological network under simulated scenarios of Nanjing in 2035. (<b>a</b>) Land use under simulated scenarios of Nanjing in 2035; (<b>b</b>) Ecological network under simulated scenarios of Nanjing in 2035; (<b>c</b>) Comparison of land-use area before and after simulation in Nanjing; (<b>d</b>) Comparison of carbon sinks and connectivity before and after simulation in Nanjing.</p>
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<p>Spatial distribution map of carbon sink capacity, efficiency, and variability for ecological sources of Nanjing in 2020.</p>
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<p>Spatial distribution map of carbon sink index for ecological sources of Nanjing in 2020.</p>
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<p>Correlation analysis between carbon sinks and connectivity for ecological sources of Nanjing.</p>
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<p>Optimization strategies of ecological network in Nanjing. (<b>a</b>) Overall plan for optimizing the ecological network in Nanjing; (<b>b</b>) Distribution map of ecological strong nodes in Nanjing; (<b>c</b>) Distribution map of ecological weak nodes in Nanjing; (<b>d</b>) Distribution map of added ecological stepping stones in Nanjing; (<b>e</b>) Distribution map of ecological conservation corridors in Nanjing; (<b>f</b>) Distribution map of ecological potential corridors in Nanjing; (<b>g</b>) Distribution map of ecological restoration corridors in Nanjing.</p>
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<p>Ternary diagram of carbon capacity-efficiency-variability for 15 weak carbon sink nodes in Nanjing.</p>
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19 pages, 359 KiB  
Review
Flaviviruses—Induced Neurological Sequelae
by Samantha Gabrielle Cody, Awadalkareem Adam, Andrei Siniavin, Sam S. Kang and Tian Wang
Pathogens 2025, 14(1), 22; https://doi.org/10.3390/pathogens14010022 - 31 Dec 2024
Viewed by 719
Abstract
Flaviviruses, a group of single-stranded RNA viruses spread by mosquitoes or ticks, include several significant neurotropic viruses, such as West Nile virus (WNV), Japanese encephalitis virus (JEV), tick-borne encephalitis virus (TBEV), and Zika virus (ZIKV). These viruses can cause a range of neurological [...] Read more.
Flaviviruses, a group of single-stranded RNA viruses spread by mosquitoes or ticks, include several significant neurotropic viruses, such as West Nile virus (WNV), Japanese encephalitis virus (JEV), tick-borne encephalitis virus (TBEV), and Zika virus (ZIKV). These viruses can cause a range of neurological diseases during acute infection, from mild, flu-like symptoms to severe and fatal encephalitis. A total of 20–50% of patients who recovered from acute flavivirus infections experienced long-term cognitive issues. Here, we discuss these major neurotropic flaviviruses-induced clinical diseases in humans and the recent findings in animal models and provide insights into the underlying disease mechanisms. Full article
(This article belongs to the Special Issue Neuropathogenesis of Arboviruses)
20 pages, 977 KiB  
Systematic Review
Therapeutic Potential of Ketogenic Interventions for Autosomal-Dominant Polycystic Kidney Disease: A Systematic Review
by Donglai Li, Jessica Dawson and Jenny E. Gunton
Nutrients 2025, 17(1), 145; https://doi.org/10.3390/nu17010145 - 31 Dec 2024
Viewed by 920
Abstract
Background: Recent findings have highlighted that abnormal energy metabolism is a key feature of autosomal-dominant polycystic kidney disease (ADPKD). Emerging evidence suggests that nutritional ketosis could offer therapeutic benefits, including potentially slowing or even reversing disease progression. This systematic review aims to synthesise [...] Read more.
Background: Recent findings have highlighted that abnormal energy metabolism is a key feature of autosomal-dominant polycystic kidney disease (ADPKD). Emerging evidence suggests that nutritional ketosis could offer therapeutic benefits, including potentially slowing or even reversing disease progression. This systematic review aims to synthesise the literature on ketogenic interventions to evaluate the impact in ADPKD. Methods: A systematic search was conducted in Medline, Embase, and Scopus using relevant Medical Subject Headings (MeSH) and keywords. Studies assessing ketogenic interventions in the management of ADPKD in both human and animal models were selected for data extraction and analysis. Results: Three animal reports and six human studies were identified. Ketogenic diets (KD) significantly slowed polycystic kidney disease (PKD) progression in rats with improved renal function and reduced cystic areas. There was reduced renal fibrosis and cell proliferation. The supplementation of beta-hydroxybutyrate (BHB) in rats also reduced PKD progression in a dose-dependent manner. Human studies (n = 129) on KD in ADPKD reported consistent body mass index (BMI) reduction across trials, with an average weight loss of ∼4 kg. Improvements in blood pressure were also noted. Ketosis was achieved in varying degrees. Effects on kidney function (eGFR) were beneficial. Results for kidney volume were mixed but most studies were underpowered for this outcome. Lipid profiles showed increases in total cholesterol (∼1 mmol/L) and LDL cholesterol (∼0.4 mmol/L) in most studies. Safety concerns such as “keto flu” symptoms, elevated uric acid levels, and occasional kidney stones were noted. Overall feasibility and adherence to the KD were rated positively by most participants. Conclusions: Human studies are promising; however, they have been limited by small sample sizes and short durations. Larger, long-term trials are needed to assess the efficacy, adherence, and safety of ketogenic diets in people with ADPKD. Full article
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<p>Pathological mechanisms of cyst formation in ADPKD. Cystogenesis in ADPKD is driven by a complex interplay of dysregulated signalling pathways. Mutations in polycystin 1/2 reduce calcium influx, consequently increasing intracellular cAMP, NFAT, and PI3K-PKB, which stimulate cell proliferation in cystic cells. These effects are mediated through the activation of the MAPK-ERK pathway. Additionally, renal expression of JAK2 and STAT is abnormally elevated in ADPKD, promoting excessive growth of renal cells. Elevated EGF and EGFR activity further drive cystogenesis by stimulating phosphorylation of the MAPK-ERK pathway and upregulating mTOR signalling. In addition, phosphorylation of AMPK, a negative regulator of mTOR, is reduced in cells lacking polycystin 1, further contributing to mTOR activation. Collectively, these disruptions in signalling pathways lead to uncontrolled cyst growth and expansion in ADPKD. ADPKD: autosomal-dominant polycystic kidney disease; AMPK: AMP-activated protein kinase; cAMP: cyclic adenosine monophosphate; EGF: epidermal growth factor; EGFR: epidermal growth factor receptor; JAK2: Janus kinase 2; MAPK: mitogen-activated protein kinases; mTOR: mammalian target of rapamycin; NFAT: nuclear factor of activated T cells; PI3K: phosphoinositide 3-kinase; PKB: protein kinase B; STAT: signal transducer and activator of transcription.</p>
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<p>PRISMA flow diagram of article selection for the systematic review.</p>
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42 pages, 31509 KiB  
Article
City Health Assessment: Urbanization and Eco-Environment Dynamics Using Coupling Coordination Analysis and FLUS Model—A Case Study of the Pearl River Delta Urban Agglomeration
by Xiangeng Peng, Liao Liao, Xiaohong Tan, Ruyi Yu and Kao Zhang
Land 2025, 14(1), 46; https://doi.org/10.3390/land14010046 - 28 Dec 2024
Viewed by 675
Abstract
Rapid urbanization in China has profoundly transformed its urban systems, bringing about considerable ecological challenges and significant imbalances between urban growth and ecological health. The Pearl River Delta (PRD) urban agglomeration, as one of China’s most economically dynamic regions, exemplifies the complex interactions [...] Read more.
Rapid urbanization in China has profoundly transformed its urban systems, bringing about considerable ecological challenges and significant imbalances between urban growth and ecological health. The Pearl River Delta (PRD) urban agglomeration, as one of China’s most economically dynamic regions, exemplifies the complex interactions between rapid urbanization and environmental sustainability. This study examined these dynamics using statistical yearbook and geographic information data from 1999 to 2018. Through a multi-scale approach integrating panel entropy, coupled coordination analysis, and FLUS models, we evaluated the relationship between urbanization and ecology at both the agglomeration and city levels. The findings revealed that while the overall coordination between urbanization and ecology in the PRD has improved, it remains at a moderate level with pronounced core-periphery disparities. Core cities face increasing ecological pressures and inefficient land use patterns. Simulation results, under three distinct policy scenarios—“unconstrained”, “growth machine”, and “compact and intensive usage/urban renewal”—and validated through field research, indicate that urban renewal presents a viable strategy for optimizing land use and mitigating ecological pressures. The study provides both a comprehensive diagnostic framework for assessing urban health and sustainability and practical intervention pathways, particularly for regions experiencing similar rapid urbanization challenges. The insights gained are especially relevant to other developing countries, offering strategies to enhance urban resilience and ecological sustainability while addressing persistent regional inequalities. Full article
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<p>Technical route for health assessment within a continuous research path from urban agglomerations to individual cities. Note: For a detailed description of the variables in Steps 1, 2, and 3 in the schematic diagram, see the implementation process explained in <a href="#sec3dot4-land-14-00046" class="html-sec">Section 3.4</a>, Implementation of Processing. For example, <math display="inline"><semantics> <mrow> <msub> <mrow> <mi mathvariant="normal">Z</mi> </mrow> <mrow> <msub> <mrow> <mi mathvariant="sans-serif">λ</mi> </mrow> <mrow> <mi mathvariant="normal">i</mi> <mi mathvariant="normal">j</mi> </mrow> </msub> </mrow> </msub> </mrow> </semantics></math> in Step 1 represents the non-dimensionalization process, followed by normalization (<math display="inline"><semantics> <mrow> <msub> <mrow> <mi mathvariant="normal">P</mi> </mrow> <mrow> <mi mathvariant="sans-serif">λ</mi> <mi mathvariant="normal">i</mi> <mi mathvariant="normal">j</mi> </mrow> </msub> </mrow> </semantics></math>), then the entropy weight method (<math display="inline"><semantics> <mrow> <msub> <mrow> <mi mathvariant="normal">E</mi> </mrow> <mrow> <mi mathvariant="normal">j</mi> </mrow> </msub> <msub> <mrow> <mo>,</mo> <mi mathvariant="normal">D</mi> </mrow> <mrow> <mi mathvariant="normal">j</mi> </mrow> </msub> <mo>,</mo> <msub> <mrow> <mi mathvariant="normal">W</mi> </mrow> <mrow> <mi mathvariant="normal">j</mi> </mrow> </msub> </mrow> </semantics></math>), and finally the calculation of the comprehensive evaluation index (<math display="inline"><semantics> <mrow> <msub> <mrow> <mi mathvariant="normal">C</mi> </mrow> <mrow> <mi mathvariant="sans-serif">λ</mi> <mi mathvariant="normal">i</mi> </mrow> </msub> </mrow> </semantics></math>). Similarly, C, T, and D in Step 2 represent the calculation of the coupling degree, coordination degree, and coupling coordination degree, respectively, while Step 3 represents the key neighborhood influence (<math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi mathvariant="sans-serif">Ω</mi> </mrow> <mrow> <mi mathvariant="normal">p</mi> <mo>,</mo> <mi mathvariant="normal">k</mi> </mrow> <mrow> <mi mathvariant="normal">t</mi> </mrow> </msubsup> </mrow> </semantics></math>), inertia coefficient (<math display="inline"><semantics> <mrow> <msubsup> <mrow> <mi>Inertial</mi> </mrow> <mrow> <mi mathvariant="normal">k</mi> </mrow> <mrow> <mi mathvariant="normal">t</mi> </mrow> </msubsup> </mrow> </semantics></math>), and total land use probability (<math display="inline"><semantics> <mrow> <mi mathvariant="normal">T</mi> <msubsup> <mrow> <mi mathvariant="normal">P</mi> </mrow> <mrow> <mi mathvariant="normal">p</mi> <mo>,</mo> <mi mathvariant="normal">k</mi> </mrow> <mrow> <mi mathvariant="normal">t</mi> </mrow> </msubsup> </mrow> </semantics></math>) in running the FLUS model.</p>
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<p>(<b>a</b>) Geographical location of the nine cities in the PRD. (<b>b</b>) Geo-economic network of Guangdong. (<b>c</b>) The level of urbanization of the population, economy, and society in Guangdong<a href="#fn001-land-14-00046" class="html-fn">1</a>.</p>
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<p>Trends of comprehensive levels of urbanization in the urban agglomeration of the PRD.</p>
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<p>Trends of comprehensive levels of eco-environment in the urban agglomeration of the PRD.</p>
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<p>Trends of comprehensive levels of coupling coordination between urbanization and eco-environment in the urban agglomeration of the PRD.</p>
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<p>Spatial evolution of urbanization system level in the urban agglomeration of the PRD.</p>
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<p>Spatial evolution of the eco-environment system level in the urban agglomeration of the PRD.</p>
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<p>Spatial evolution of coupling coordination between urbanization and eco-environment in the urban agglomeration of the PRD.</p>
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<p>Typical example of coupling and coordination from within the system between urbanization and eco-environment in the urban agglomeration of the PRD. (<b>a</b>) Guangzhou; (<b>b</b>) Shenzhen; (<b>c</b>) Dongguan; (<b>d</b>) Foshan; (<b>e</b>) Zhuhai; (<b>f</b>) Zhongshan; (<b>g</b>) Jiangmen; (<b>h</b>) Huizhou; (<b>i</b>) Zhaoqing. Note: In each subplot, the shaded area (referring to the interval from -1 to 1 on the right vertical axis) identifies the range where the difference between the comprehensive development levels of indicators within the urbanization and eco-environmental subsystems is considered coordinated. A value exceeding 1 indicates over-development of the minuend indicator compared to the subtrahend indicator, while a value below -1 indicates the opposite - both situations represent uncoordinated states.</p>
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<p>Land-use transfer matrix of Guangzhou (2000–2018).</p>
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<p>Driving factors of urban land-use change in Guangzhou.</p>
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<p>Construction land-use probability of occurrence in Guangzhou.Note: The left subplot represents the suitability probability for construction land, and the right subplot represents the suitability probability for non-construction land, with darker warm colors indicating higher suitability.</p>
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<p>Comparison of the current land-use status and the simulation results of multiple policy scenarios in Guangzhou from 2000 to 2025.</p>
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<p>Comparison of the simulation results of multiple policy scenarios in Guangzhou in 2025.</p>
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<p>(<b>a</b>) Distribution of urban village renovation projects in Guangzhou. (<b>b</b>) Area of urban village renovation and number of projects in Guangzhou’s 11 districts.</p>
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<p>A typical case of a fully renovated urban village in Guangzhou. (<b>a</b>) Liede Village before renewal; (<b>b</b>) Liede Village after renewal; (<b>c</b>) Yangji Village before renewal; (<b>d</b>) Yangji Village after renewal; (<b>e</b>) Pazhou Village before renewal; (<b>f</b>) Pazhou Village after renewal.</p>
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<p>A typical case of a fully renovated urban village in Guangzhou. (<b>a</b>) Liede Village before renewal; (<b>b</b>) Liede Village after renewal; (<b>c</b>) Yangji Village before renewal; (<b>d</b>) Yangji Village after renewal; (<b>e</b>) Pazhou Village before renewal; (<b>f</b>) Pazhou Village after renewal.</p>
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<p>Urban renewal as a paradigm for sustainable development.</p>
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21 pages, 5843 KiB  
Article
Mucosal Immunization with an Influenza Vector Carrying SARS-CoV-2 N Protein Protects Naïve Mice and Prevents Disease Enhancement in Seropositive Th2-Prone Mice
by Mariia V. Sergeeva, Kirill Vasilev, Ekaterina Romanovskaya-Romanko, Nikita Yolshin, Anastasia Pulkina, Daria Shamakova, Anna-Polina Shurygina, Arman Muzhikyan, Dmitry Lioznov and Marina Stukova
Vaccines 2025, 13(1), 15; https://doi.org/10.3390/vaccines13010015 - 28 Dec 2024
Viewed by 791
Abstract
Background/Objectives: Intranasal vaccination enhances protection against respiratory viruses by providing stimuli to the immune system at the primary site of infection, promoting a balanced and effective response. Influenza vectors with truncated NS1 are a promising vaccine approach that ensures a pronounced local CD8+ [...] Read more.
Background/Objectives: Intranasal vaccination enhances protection against respiratory viruses by providing stimuli to the immune system at the primary site of infection, promoting a balanced and effective response. Influenza vectors with truncated NS1 are a promising vaccine approach that ensures a pronounced local CD8+ T-cellular immune response. Here, we describe the protective and immunomodulating properties of an influenza vector FluVec-N carrying the C-terminal fragment of the SARS-CoV-2 nucleoprotein within a truncated NS1 open reading frame. Methods: We generated several FluVec-N recombinant vectors by reverse genetics and confirmed the vector’s genetic stability, antigen expression in vitro, attenuation, and immunogenicity in a mouse model. We tested the protective potential of FluVec-N intranasal immunization in naïve mice and seropositive Th2-prone mice, primed with aluminium-adjuvanted inactivated SARS-CoV-2. Immune response in immunized and challenged mice was analyzed through serological methods and flow cytometry. Results: Double intranasal immunization of naïve mice with FluVec-N reduced weight loss and viral load in the lungs following infection with the SARS-CoV-2 beta variant. Mice primed with alum-adjuvanted inactivated coronavirus experienced substantial early weight loss and eosinophilia in the lungs during infection, demonstrating signs of enhanced disease. A single intranasal boost immunization with FluVec-N prevented the disease enhancement in primed mice by modulating the local immune response. Protection was associated with the formation of specific IgA and the early activation of virus-specific effector and resident CD8+ lymphocytes in mouse lungs. Conclusions: Our study supports the potential of immunization with influenza vector vaccines to prevent respiratory diseases and associated immunopathology. Full article
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<p>The NS gene structure of the recombinant FluVec-N virus and expression of the chimeric NS1<sub>124</sub>_N protein. (<b>a</b>) Proteins encoded by two ORFs in the NS gene. (<b>b</b>) Western blot of infected cell lysates probed with anti-NS1 antibody. Viruses are indicated at the top; molecular weight marker is shown in kDa. (<b>c</b>) Immunofluorescent microscopy images of infected cells probed with anti-influenza NP antibody (A–D) and anti-SARS-CoV-2 N protein antibody (E–H). Viruses are indicated above the panel. The original images can be found in the <a href="#app1-vaccines-13-00015" class="html-app">Supplementary Materials</a>.</p>
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<p>The recombinant FluVec-N virus is attenuated and immunogenic in C57 mice. (<b>a</b>) Weight dynamics of mice intranasally inoculated with the indicated viruses, shown as percent of the initial weight (M ± SD). (<b>b</b>) Survival of mice intranasally inoculated with the indicated viruses. (<b>c</b>) T-cell immune response in mouse lungs to the influenza NP (366–374) peptide (left) or the SARS-CoV-2 N-protein (right) 10 days after immunization with the indicated virus. Relative content of total (upper panel) and individual (lower panel) subpopulations of cytokine-producing effector CD8+ T lymphocytes. Data obtained after subtracting background values of the relative content of cytokine-producing cells in the unstimulated control are presented. Statistical analysis was performed using ANOVA (<span class="html-italic">p</span> &lt; 0.0001), followed by pairwise group comparison using Tukey’s test. * <span class="html-italic">p</span> &lt; 0.05 marks significant differences with the DPBS control group.</p>
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<p>Protection experiments in BALB/c mice. (<b>a</b>) Study design. Immunization schemes for experimental groups are listed in the lower left, FI—formalin-inactivated. (<b>b</b>) Neutralizing SARS-CoV-2 antibodies in serum after second immunization. (<b>c</b>) N-protein specific antibodies in BAL after second immunization, sample dilution 1/2. (<b>d</b>) N-protein specific antibodies in BAL after challenge, sample dilution 1/2. ANOVA (<span class="html-italic">p</span> &lt; 0.0001) was followed by Dunnette’s test for multiple comparisons of each group with placebo: ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001, **** <span class="html-italic">p</span> &lt; 0.0001.</p>
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<p>Protection experiments in BALB/c mice. (<b>a</b>,<b>b</b>) Infectious titers in BAL and the nasal turbinates (NTs) of challenged mice at 5 dpi. (<b>c</b>,<b>d</b>) Virus RNA in BAL and NTs of challenged mice at 5 dpi. Individual values and group means are presented. ANOVA (<span class="html-italic">p</span> &lt; 0.0001) was followed by Dunnette’s test for multiple comparisons of each group with placebo: * <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001, **** <span class="html-italic">p</span> &lt; 0.0001. (<b>e</b>) Body weight of challenged mice during a week after infection. Group means with 95% confidence intervals are presented. (<b>f</b>) Histopathological summary score of lung examination at 7 dpi. Individual values and group means are presented. The dotted line corresponds to the mean value for the placebo (infection control) group. (<b>g</b>) Microphotographs of the most pronounced pathological changes in bronchioles (upper panel) and blood vessels (lower panel) in the mouse lungs at 7 dpi, 400×.</p>
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<p>Innate immunity populations in the lungs of vaccinated BALB/c mice upon subsequent infection with SARS-CoV-2. (<b>a</b>) Alveolar macrophages; (<b>b</b>) interstitial macrophages; (<b>c</b>) monocytes; (<b>d</b>) dendritic cells; (<b>e</b>) eosinophils; (<b>f</b>) natural killers. Percentages of different cell types in the population of lung CD45+ cells are presented individually for each animal, and the horizontal line represents the group mean. An intact group is presented for comparison with normal non-infected mice. * <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001, **** <span class="html-italic">p</span> &lt; 0.0001 calculated using Tukey post-hoc test following one-way ANOVA applied to log values (<span class="html-italic">p</span> &lt; 0.0001).</p>
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<p>Main populations of CD4+ and CD8+ memory T lymphocytes in BALB/c mouse lung tissue 5 days after infection. (<b>a</b>,<b>b</b>) Total tissue-resident memory cells (CD4/CD8+CD44+CD62L-CD103+CD69+); (<b>c</b>,<b>d</b>) N-specific cytokine-producing tissue-resident memory cells; (<b>e</b>,<b>f</b>) N-specific cytokine-producing effector memory cells. Percentages of cells in the corresponding population are presented individually for each animal, and the horizontal line represents the group mean. An intact group is presented for comparison with normal non-infected mice. * <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001, **** <span class="html-italic">p</span> &lt; 0.0001 calculated using Tukey post-hoc test following one-way ANOVA applied to log values (<span class="html-italic">p</span> &lt; 0.0001).</p>
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<p>Gating strategy to identify innate immune cell populations.</p>
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<p>Gating strategy to identify adaptive immunity cell populations.</p>
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<p>Genetic stability of the FluVec-N chimeric NS gene. The whole-length RT-PCR amplification products are presented; pl—gene amplicon from the control plasmid. (<b>a</b>) Length of the NS gene segment of the virus clones from the 3rd passage of the FluVec-N (H1N1) recombinant virus carrying HA and NA from the A/PR/8/34 (H1N1) strain; (<b>b</b>) Length of the NS gene segment of the virus clones from the 2nd, 3rd, and 6th passages of the recombinant FluVec-N (H1N1pdm09) virus carrying HA and NA from the A/Guangdong-Maonan/SWL1536/2019 (H1N1pdm09) strain. The original images can be found in <a href="#app1-vaccines-13-00015" class="html-app">Supplementary Materials</a>.</p>
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<p>CD4+ T-cell response to the influenza NP (366–374) peptide and the SARS-CoV-2 N-protein in the lungs of immunized mice. Relative content of total (upper panel) and individual (lower panel) subpopulations of cytokine-producing effector CD4+ T lymphocytes was assessed 10 days after immunization with the indicated viruses. Data obtained after subtracting background values of the relative content of cytokine-producing cells in the unstimulated control are presented. Statistical analysis was performed using ANOVA (<span class="html-italic">p</span> &lt; 0.0001) followed by pairwise group comparison using Tukey’s test. * <span class="html-italic">p</span> &lt; 0.05 marks significant differences with the DPBS control group.</p>
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<p>Relative content of individual subpopulations of cytokine-producing resident CD4+ and CD8+ T lymphocytes. Data obtained after subtracting background values of the relative content of cytokine-producing cells in the unstimulated control are presented. Statistical analysis was performed using ANOVA (<span class="html-italic">p</span> &lt; 0.0001) followed by pairwise group comparison using Tukey’s test. * <span class="html-italic">p</span> &lt; 0.05 marks significant differences with the placebo control group.</p>
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<p>Relative content of individual subpopulations of cytokine-producing effector memory CD4+ and CD8+ T lymphocytes. Data obtained after subtracting background values of the relative content of cytokine-producing cells in the unstimulated control are presented. Statistical analysis was performed using ANOVA (<span class="html-italic">p</span> &lt; 0.0001) followed by pairwise group comparison using Tukey’s test. * <span class="html-italic">p</span> &lt; 0.05 marks significant differences with the placebo control group.</p>
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25 pages, 13655 KiB  
Article
Monitoring Spatial-Temporal Variability of Vegetation Coverage and Its Influencing Factors in the Yellow River Source Region from 2000 to 2020
by Boyang Wang, Jianhua Si, Bing Jia, Xiaohui He, Dongmeng Zhou, Xinglin Zhu, Zijin Liu, Boniface Ndayambaza and Xue Bai
Remote Sens. 2024, 16(24), 4772; https://doi.org/10.3390/rs16244772 - 21 Dec 2024
Viewed by 550
Abstract
As a vital conservation area for water sources in the Yellow River Basin, understanding the spatial-temporal dynamics of vegetation coverage is crucial, along with the factors that affect it, to ensure ecological preservation and sustainable development of the Yellow River Source Region (YRSR). [...] Read more.
As a vital conservation area for water sources in the Yellow River Basin, understanding the spatial-temporal dynamics of vegetation coverage is crucial, along with the factors that affect it, to ensure ecological preservation and sustainable development of the Yellow River Source Region (YRSR). In this paper, we utilized Landsat surface reflectance data from 2000 to 2020 using de-clouding and masking methods implementing the Google Earth Engine (GEE) cloud platform. We investigated spatial-temporal changes in vegetation coverage by combining the maximum value composite (MVC), the dimidiate pixel model (DPM), the Theil–Sen median slope, and the Mann–Kendall test. The influencing factors on vegetation coverage were quantitatively analyzed using a geographic detector, and future tendencies in vegetation coverage were predicted utilizing the Future Land Use Simulation (FLUS) model. The outcomes suggested the following: (1) On the temporal scale, vegetation coverage exhibited a general upward trend between 2000 and 2020, with the YRSR showing a yearly growth rate of 0.23% (p < 0.001). In comparison to 2000, the area designated as having extremely high vegetation coverage increased by 19.3% in 2020. (2) Spatially, the central and southeast regions have higher values of vegetation coverage, whereas the northwest has lower values. In the study area, 75.5% of the region demonstrated a significant improvement trend, primarily in Xinghai County, Zeku County, and Dari County in the south and the northern portion of the YRSR; conversely, a notable tendency of degradation was identified in 11.8% of the area, mostly in the southeastern areas of Qumalai County, Chenduo County, Shiqu County, and scattered areas in the southeastern region. (3) With an explanatory power of exceeding 45%, the three influencing factors that had the biggest effects on vegetation coverage were mean annual temperature, elevation, and mean annual precipitation. Mean annual precipitation has been shown to have a major impact on vegetation covering; the interconnections involving these factors have increased the explanatory power of vegetation coverage’s regional distribution. (4) Predictions for 2030 show that the vegetation coverage is trending upward in the YRSR, with a notable recovery trend in the northwestern region. This study supplies a theoretical foundation to formulate strategies to promote sustainable development and ecological environmental preservation in the YRSR. Full article
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<p>Location of the study area.</p>
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<p>Influencing factors of vegetation coverage. Note: (<b>a</b>) Mean annual temperature, (<b>b</b>) Mean annual precipitation, (<b>c</b>) Elevation, (<b>d</b>) Vegetation type, (<b>e</b>) Snow cover, (<b>f</b>) Solar radiation, (<b>g</b>) Soil moisture, (<b>h</b>) Vapor pressure deficit, (<b>i</b>) Land use and land cover, (<b>j</b>) Livestock capacity, (<b>k</b>) Density of population.</p>
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<p>Trend of mean FVC in the Yellow River Source Region (YRSR) from 2000 to 2020.</p>
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<p>Proportions of different levels of vegetation coverage in the YRSR.</p>
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<p>Spatial distribution characteristics of FVC in the YRSR.</p>
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<p>Spatial distribution of FVC trends, 2000–2020.</p>
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<p>Changes in the center of gravity migration of vegetation coverage grades, 2000–2020.</p>
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<p>Factors interaction detection.</p>
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<p>Future trends in FVC in the YRSR.</p>
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26 pages, 6096 KiB  
Article
Evolution of Vegetation Coverage in the Jinan Section of the Basin of the Yellow River (China), 2008–2022: Spatial Dynamics and Drivers
by Dongling Ma, Zhenxin Lin, Qian Wang, Yifan Yu, Qingji Huang and Yingwei Yan
Forests 2024, 15(12), 2219; https://doi.org/10.3390/f15122219 - 16 Dec 2024
Viewed by 663
Abstract
The Yellow River Basin serves as a critical ecological barrier in China. However, it has increasingly faced severe ecological and environmental challenges, with soil erosion and overgrazing being particularly prominent issues. As an important region in the middle and lower reaches of the [...] Read more.
The Yellow River Basin serves as a critical ecological barrier in China. However, it has increasingly faced severe ecological and environmental challenges, with soil erosion and overgrazing being particularly prominent issues. As an important region in the middle and lower reaches of the Yellow River, the Jinan section of the Yellow River Basin is similarly affected by these problems, posing significant threats to the stability and sustainability of its ecosystems. To scientifically identify areas severely impacted by soil erosion and systematically quantify the effects of climate change on vegetation coverage within the Yellow River Basin, this study focuses on the Jinan section. By analyzing the spatio-temporal evolution patterns of the Normalized Difference Vegetation Index (NDVI), this research aims to explore the driving mechanisms behind these changes and further predict the future spatial distribution of NDVI, providing theoretical support and practical guidance for regional ecological conservation and sustainable development. This study employed the slope trend analysis method to examine the spatio-temporal variation characteristics of NDVI in the Jinan section of the Yellow River Basin from 2008 to 2022 and utilized the FLUS model to predict the spatial distribution of NDVI in 2025. The Optimal Parameters-based Geographical Detector (OPGD) model was applied to systematically analyze the impacts of four key driving factors—precipitation (PRE), temperature (TEM), population density (POP), and gross domestic product (GDP) on vegetation coverage. Finally, correlation and lag effect analyses were conducted to investigate the relationships between NDVI and TEM as well as NDVI and PRE. The research results indicate the following: (1) from 2008 to 2022, the NDVI values during the growing season in the Jinan section of the Yellow River Basin exhibited a significant increasing trend. This growth suggests a continuous improvement in regional vegetation coverage, likely influenced by the combined effects of natural and anthropogenic factors. (2) The FLUS model predicts that, by 2025, the proportion of high-density NDVI areas will rise to 55.35%, reflecting the potential for further optimization of vegetation coverage under appropriate management. (3) POP had a particularly significant impact on vegetation coverage, and its interaction with TEM, PRE, and GDP generated an amplified combined effect, indicating the dominant role of the synergy between socioeconomic and climatic factors in regional vegetation dynamics. (4) NDVI exhibited a significant positive correlation with both temperature and precipitation, further demonstrating that climatic conditions were key drivers of vegetation coverage changes. (5) In urban areas, NDVI showed a certain time lag in response to changes in precipitation and temperature, whereas this lag effect was not significant in suburban and mountainous areas, highlighting the regulatory role of human activities and land use patterns on vegetation dynamics in different regions. These findings not only reveal the driving mechanisms and influencing factors behind vegetation coverage changes but also provide critical data support for ecological protection and economic development planning in the Yellow River Basin, contributing to the coordinated advancement of ecological environment construction and economic growth. Full article
(This article belongs to the Section Forest Ecology and Management)
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<p>Study area. (<b>a</b>) China, (<b>b</b>) The Yellow River Basin, and (<b>c</b>) The Jinan Section of the Yellow River Basin.</p>
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<p>Flow chart of the study.</p>
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<p>Temporal variation characteristics of NDVI.</p>
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<p>The percentage of NDVI change trend during the planting season.</p>
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<p>Spatial distribution of NDVI trends. (<b>a</b>) 2008–2012, (<b>b</b>) 2013–2017, (<b>c</b>) 2018–2022, and (<b>d</b>) 2008–2022.</p>
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<p>Comparison of NDVI Distribution Between 2022 and 2025. (<b>a</b>) 2022, (<b>b</b>) 2025.</p>
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<p>Percentage Distribution of NDVI in 2022 and 2025.</p>
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<p>NDVI Conversion Relationships.</p>
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<p>Explanatory power of interactive detection of driving factors. (<b>a</b>) 2008, (<b>b</b>) 2013, (<b>c</b>) 2018, and (<b>d</b>) 2022.</p>
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<p>Percentage of correlation between NDVI and rainfall.</p>
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<p>Spatial distribution of the correlation analysis between NDVI and PRE. (<b>a</b>) 2008–2012, (<b>b</b>) 2013–2017, (<b>c</b>) 2018-2022, and (<b>d</b>) 2008–2022.</p>
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<p>Percentage of correlation between NDVI and TEM.</p>
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<p>Spatial distribution of the correlation analysis between NDVI and TEM. (<b>a</b>) 2008–2012, (<b>b</b>) 2013–2017, (<b>c</b>) 2018–2022, and (<b>d</b>) 2008–2022.</p>
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<p>Spatial distribution of the lagged relationship between NDVI and TEM in summer. (<b>a</b>) Current Month, (<b>b</b>) One Month Prior, and (<b>c</b>) Two Month Prior.</p>
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<p>Spatial distribution of the lagged relationship between NDVI and TEM in summer. (<b>a</b>) Current Month, (<b>b</b>) One Month Prior, and (<b>c</b>) Two Month Prior.</p>
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17 pages, 47180 KiB  
Article
Multi-Scenario Simulation of Urban–Rural Land Use Spatial Reconstruction in Highly Urbanized Areas: A Case Study from the Southern Jiangsu Region
by Changjun Jiang and Huiguang Chen
Land 2024, 13(12), 2199; https://doi.org/10.3390/land13122199 - 16 Dec 2024
Cited by 1 | Viewed by 658
Abstract
China’s rural population flowing into highly urbanized areas has led to the spatial reconstruction of urban–rural land use. Exploring the laws and trends of urban–rural land use in highly urbanized areas is of great significance in promoting rural transformation. This paper takes the [...] Read more.
China’s rural population flowing into highly urbanized areas has led to the spatial reconstruction of urban–rural land use. Exploring the laws and trends of urban–rural land use in highly urbanized areas is of great significance in promoting rural transformation. This paper takes the southern Jiangsu region as a research area and uses a system dynamics (SD) model to simulate the demand for different land types based on economic, social, policy, and environmental (ESPE) factors. Future land use simulation (FLUS) is used to simulate the spatial evolution trend of urban–rural land use based on point–axis elements. The results show that the agricultural production space is severely squeezed by the urban living space. Under the scenario of rapid expansion, the decrease in arable land quantity and the demand area for rural residential areas are the largest. Under the scenario of high-quality development, the decrease in arable land area and the demand for land in rural residential areas are lowest. Based on the spatial simulation, it is reported that the areas with more intense land use spatial reconstruction in the three scenarios are mainly concentrated in the region’s urban–rural border areas. The future evolution of urban–rural land is summarized into three models: (1) single-center-driving expansion, (2) patchy expansion near the city center, and (3) multi-center-driving expansion. This paper proposes targeted policy recommendations to provide a scientific reference for solving the conflict between urban and rural land use. Full article
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<p>Theoretical framework.</p>
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<p>Study area.</p>
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<p>Simulation process based on the SD-FLUS model.</p>
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<p>Spatial distribution of land use in southern Jiangsu.</p>
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<p>Flowchart of SD model for predicting land demand in southern Jiangsu.</p>
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<p>Relative error between actual area and simulated area.</p>
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<p>Simulated changes in the area of various land types in 2035.</p>
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<p>Land use spatial layout under different scenarios in southern Jiangsu in 2035.</p>
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<p>Simulation of rural land use spatial reconstruction in typical regions by 2035.</p>
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<p>Urban–rural land use restructuring models in southern Jiangsu in 2035.</p>
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