[go: up one dir, main page]
More Web Proxy on the site http://driver.im/
You seem to have javascript disabled. Please note that many of the page functionalities won't work as expected without javascript enabled.
 
 
Sign in to use this feature.

Years

Between: -

Subjects

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Journals

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Article Types

Countries / Regions

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Search Results (2,058)

Search Parameters:
Keywords = land restoration

Order results
Result details
Results per page
Select all
Export citation of selected articles as:
23 pages, 4494 KiB  
Review
Conservation Biodiversity in Arid Areas: A Review
by Voichita Timis-Gansac, Lucian Dinca, Cristinel Constandache, Gabriel Murariu, Gabriel Cheregi and Claudia Simona Cleopatra Timofte
Sustainability 2025, 17(6), 2422; https://doi.org/10.3390/su17062422 - 10 Mar 2025
Viewed by 189
Abstract
Drylands cover a vast area, and biodiversity conservation in these regions represents a major challenge. A bibliometric study of published research highlighted several key aspects, including publication types, research fields, years of publication, contributing countries, institutions, languages, journals, publishers, authors, and frequently used [...] Read more.
Drylands cover a vast area, and biodiversity conservation in these regions represents a major challenge. A bibliometric study of published research highlighted several key aspects, including publication types, research fields, years of publication, contributing countries, institutions, languages, journals, publishers, authors, and frequently used keywords. The analysis also included plants related to biodiversity conservation in arid areas, animals related to biodiversity conservation in arid areas, and causes of biodiversity decline in arid regions, effects of biodiversity loss in these regions, and restoration methods aimed at improving biodiversity conservation in arid areas. A total of 947 publications were identified, starting from 1994, authored by researchers from 99 countries, primarily from Australia, the USA, China, Spain, and South Africa, and published in 345 journals, with the most prominent being Journal of Arid Environments, Biodiversity and Conservation, and Biological Conservation. The most commonly appearing keywords included biodiversity, conservation, diversity, vegetation, and patterns, with recent years showing an increased use of terms related to the causes and effects of aridification: climate change, land use, and ecosystem services. The causes of biodiversity loss in drylands are primarily linked to human activities and climatic changes, while the effects impact the entire ecosystem. Methods to improve biodiversity include traditional agroforestry systems, tree plantations and other plant species, grazing management, and other approaches. Combined actions among stakeholders and ecologically appropriate nature-based solutions are also recommended. Improvements in conservation biodiversity in arid areas are very important also for achieving the sustainability goals in these areas. However, numerous aspects of this topic remain to be studied in greater detail. Full article
(This article belongs to the Special Issue Biodiversity, Biologic Conservation and Ecological Sustainability)
Show Figures

Figure 1

Figure 1
<p>Used methodology.</p>
Full article ">Figure 2
<p>(<b>a</b>) The distribution of the main types of publications concerning conservation of biodiversity in arid areas; (<b>b</b>) the distribution of the main research areas of publications used in the bibliometric analysis; (<b>c</b>) the distribution per year of articles concerning conservation of biodiversity in arid areas; (<b>d</b>) countries with authors who contributed to studies on the subject of biodiversity conservation in arid areas.</p>
Full article ">Figure 3
<p>Clusters of nations based on the authorship of studies related to conservation and biodiversity in arid areas.</p>
Full article ">Figure 4
<p>The primary journals publishing research on conservation of biodiversity in arid areas.</p>
Full article ">Figure 5
<p>The distribution of citations and published articles in the Biodiversity and Conservation Journal; (<b>a</b>) histogram of the number of articles by year of publication; (<b>b</b>) histogram of the distribution by year of the number of citations in the WOS Core database; (<b>c</b>) histogram of the distribution by year of the number of citations in all WOS databases; (<b>d</b>) boxplot of the number of citations by year.</p>
Full article ">Figure 6
<p>The distribution of citations and published articles in the Journal of Arid Environments; (<b>a</b>) histogram of the number of articles by year of publication; (<b>b</b>) histogram of the distribution by year of the number of citations in the WOS Core database; (<b>c</b>) histogram of the distribution by year of the number of citations in all WOS databases; (<b>d</b>) boxplot of the number of citations by year.</p>
Full article ">Figure 7
<p>Authors’ keywords concerning conservation of biodiversity in arid areas.</p>
Full article ">Figure 8
<p>Annual distribution of keywords related to conservation of biodiversity in arid areas.</p>
Full article ">
27 pages, 9188 KiB  
Article
Construction and Zoning of Ecological Security Patterns in Yichang City
by Qi Zhang, Yi Sun, Diwei Tang, Hu Cheng and Yi Tu
Sustainability 2025, 17(6), 2354; https://doi.org/10.3390/su17062354 - 7 Mar 2025
Viewed by 239
Abstract
The study of ecological security patterns is of great significance to the balance between regional economic development and environmental protection. By optimizing the regional ecological security pattern through reasonable land-use planning and resource management strategies, the purpose of maintaining ecosystem stability and improving [...] Read more.
The study of ecological security patterns is of great significance to the balance between regional economic development and environmental protection. By optimizing the regional ecological security pattern through reasonable land-use planning and resource management strategies, the purpose of maintaining ecosystem stability and improving ecosystem service capacity can be achieved, and ultimately regional ecological security can be achieved. As a typical ecological civilization city in the middle reaches of the Yangtze River, Yichang City is also facing the dual challenges of urban expansion and environmental pressure. The construction and optimization of its ecological security pattern is the key to achieving the harmonious coexistence of economic development and environmental protection and ensuring regional sustainable development. Based on the ecological environment characteristics and land-use data of Yichang City, this paper uses morphological spatial pattern analysis and landscape connectivity analysis to identify core ecological sources, constructs a comprehensive ecological resistance surface based on the sensitivity–pressure–resilience (SPR) model, and combines circuit theory and Linkage Mapper tools to extract ecological corridors, ecological pinch points, and ecological barrier points and construct the ecological security pattern of Yichang City with ecological elements of points, lines, and surfaces. Finally, the community mining method was introduced and combined with habitat quality to analyze the spatial topological structure of the ecological network in Yichang City and conduct ecological security zoning management. The following conclusions were drawn: Yichang City has a good ecological background value. A total of 64 core ecological sources were screened out with a total area of 3239.5 km². In total, 157 ecological corridors in Yichang City were identified. These corridors were divided into 104 general corridors, 42 important corridors, and 11 key corridors according to the flow centrality score. In addition, 49 key ecological pinch points and 36 ecological barrier points were identified. The combination of these points, lines, and surfaces formed the ecological security pattern of Yichang City. Based on the community mining algorithm in complex networks and the principle of Thiessen polygons, Yichang City was divided into five ecological functional zones. Among them, Community No. 2 has the highest ecological security level, high vegetation coverage, close distribution of ecological sources, a large number of corridors, and high connectivity. Community No. 5 has the largest area, but it contains most of the human activity space and construction and development zones, with low habitat quality and severely squeezed ecological space. In this regard, large-scale ecological restoration projects should be implemented, such as artificial wetland construction and ecological island establishment, to supplement ecological activity space and mobility and enhance ecosystem service functions. This study aims to construct a multi-scale ecological security pattern in Yichang City, propose a dynamic zoning management strategy based on complex network analysis, and provide a scientific basis for ecological protection and restoration in rapidly urbanizing areas. Full article
Show Figures

Figure 1

Figure 1
<p>Overview of the study area.</p>
Full article ">Figure 2
<p>Ecological security pattern framework of Yichang City.</p>
Full article ">Figure 3
<p>Principle of Louvain algorithm.</p>
Full article ">Figure 4
<p>Ecological source identification.</p>
Full article ">Figure 5
<p>Resistance factor distribution.</p>
Full article ">Figure 5 Cont.
<p>Resistance factor distribution.</p>
Full article ">Figure 6
<p>Comprehensive ecological resistance surface.</p>
Full article ">Figure 7
<p>Ecological corridors and ecological flow channels in Yichang City.</p>
Full article ">Figure 8
<p>Identification of ecological pinch points in the study area.</p>
Full article ">Figure 9
<p>Identification of ecological obstacle points under different search radius.</p>
Full article ">Figure 10
<p>Distribution of ecological obstacles under two modes.</p>
Full article ">Figure 11
<p>Distribution of ecological security patterns in Yichang City.</p>
Full article ">Figure 12
<p>Habitat quality distribution map of Yichang City.</p>
Full article ">Figure 13
<p>Classification and distribution of ecological source communities.</p>
Full article ">
40 pages, 12394 KiB  
Article
Simulative Modeling of Psychologically Acceptable Architectural and Urban Environments Combining Biomimicry Approach and Concept of Architectural/Urban Genotype as Unifying Theories
by Kęstutis Zaleckis, Indrė Gražulevičiūtė-Vileniškė and Gediminas Viliūnas
Urban Sci. 2025, 9(3), 75; https://doi.org/10.3390/urbansci9030075 - 7 Mar 2025
Viewed by 181
Abstract
This research explores the integration of biomimicry and architectural/urban genotype concepts to model psychologically acceptable environments. Drawing on foundational psychological theories—Gestalt, Attention Restoration, Prospect-Refuge, and Environmental Psychology—this study examines the private–public interface at the various urban resolutions, encompassing land plots, buildings, and urban [...] Read more.
This research explores the integration of biomimicry and architectural/urban genotype concepts to model psychologically acceptable environments. Drawing on foundational psychological theories—Gestalt, Attention Restoration, Prospect-Refuge, and Environmental Psychology—this study examines the private–public interface at the various urban resolutions, encompassing land plots, buildings, and urban structures. Biomimicry serves as a unifying framework, linking these theories with principles derived from natural systems to create sustainable and psychologically beneficial designs. The methodology incorporates simulative modeling, employing space syntax and isovist analysis to quantify key spatial features such as proximity, complexity, and refuge. This study evaluates traditional historical architectures from diverse cultural contexts, such as Islamic medina, Medieval European town, and modernist urbanism, to identify patterns of spatial organization that balance human psychological needs and ecological sustainability. Findings highlight the fractal and hierarchical nature of spatial structures and the importance of integrating human-scale, culturally relevant designs into modern urban planning. By establishing a replicable framework, this research aims to bridge theoretical and practical gaps in environmental psychology, biomimicry, and urban design, paving the way for resilient and adaptive environments that harmonize ecological and human well-being. Full article
Show Figures

Figure 1

Figure 1
<p>Visual representation of the interconnections between the psychological theories and the features of natural systems grounding the idea of biomimicry as a unifying concept in this research.</p>
Full article ">Figure 2
<p>Space Syntax analysis for three cities (Cracow, Poland; Sfax, Tunisia; Elektrėnai, Lithuania). Red colors show high and blue colors show low numerical values. Specific terms: bazzars—markets in the Islamic city, funduqs—commercial spaces, serving the needs of merchants for lodging, storage, and security.</p>
Full article ">Figure 3
<p>Comparison of space syntax normalized indicators representing six aspects of the acceptable spatial environment in the cities.</p>
Full article ">Figure 4
<p>Comparison of space syntax normalized indicators representing six aspects of the acceptable spatial environment inside houses.</p>
Full article ">Figure 5
<p>Summarizing matrix of the comparison of both cities and living houses. Red color means high, yellow—mean, and blue—low values.</p>
Full article ">Figure A1
<p>Results of the space syntax modeling of Sfax urban structure. Red color marks values equal and bigger than 1 standard deviation and blue marks minus 1 standard deviation, thus pointing out accordingly 15.9 percent of the highest and the lowest values.</p>
Full article ">Figure A2
<p>Results of the space syntax modeling of Sfax buildings (building 1 at top line). Red color marks values equal and bigger than 1 standard deviation and blue marks minus 1 standard deviation, thus pointing out accordingly 15.9 percent of the highest and the lowest values.</p>
Full article ">Figure A3
<p>Results of the space syntax modeling of Cracow urban structure. Red color marks values equal and bigger than 1 standard deviation and blue marks minus 1 standard deviation, thus pointing out accordingly 15.9 percent of the highest and the lowest values.</p>
Full article ">Figure A4
<p>Results of the space syntax modeling of Cracow buildings (building 1 at top line). Red color marks values equal and bigger than 1 standard deviation and blue marks minus 1 standard deviation, thus pointing out accordingly 15.9 percent of the highest and the lowest values.</p>
Full article ">Figure A5
<p>Results of the space syntax modeling of Elektrėnai urban structure. Red color marks values equal and bigger than 1 standard deviation and blue marks minus 1 standard deviation, thus pointing out accordingly 15.9 percent of the highest and the lowest values.</p>
Full article ">Figure A6
<p>Results of the space syntax modeling of Elektrėnai flats (buildings) (building 1 at top line). Red color marks values equal and bigger than 1 standard deviation and blue marks minus 1 standard deviation, thus pointing out accordingly 15.9 percent of the highest and the lowest values.</p>
Full article ">Figure A7
<p>Intensity, Relativized Entropy, and Choice within radius n for Sfax axial graph. Red colors show high and blue colors show low numerical values.</p>
Full article ">Figure A8
<p>Intensity, Relativized Entropy, and Choice within radius n for Cracow axial graph. Red colors show high and blue colors show low numerical values.</p>
Full article ">Figure A9
<p>Intensity, Relativized Entropy, and Choice within radius n for Elektrėnai axial graph. Red colors show high and blue colors show low numerical values.</p>
Full article ">
8 pages, 1883 KiB  
Case Report
Spontaneous Rupture of the Internal Iliac Artery in an Elderly Patient: A Case Report Exploring the Possible Role of Klebsiella Pneumoniae Infection
by David Pakeliani, Giuseppe Indelicato, Liborio Ferrante and Maurizio Finocchiaro
Int. J. Transl. Med. 2025, 5(1), 10; https://doi.org/10.3390/ijtm5010010 - 6 Mar 2025
Viewed by 183
Abstract
Background: The spontaneous rupture of the internal iliac artery (IIA) is an exceedingly rare vascular event, typically associated with congenital anomalies or degenerative conditions. This report details an unprecedented case of isolated IIA rupture in an elderly patient with evidence of plaque rupture [...] Read more.
Background: The spontaneous rupture of the internal iliac artery (IIA) is an exceedingly rare vascular event, typically associated with congenital anomalies or degenerative conditions. This report details an unprecedented case of isolated IIA rupture in an elderly patient with evidence of plaque rupture but devoid of congenital vascular pathology. Case Presentation: An 81-year-old Caucasian male presented to the Emergency Department following a syncopal episode and acute right iliac fossa pain. His significant medical history was atrial fibrillation managed with anticoagulation (Apixaban), non-insulin-dependent diabetes mellitus, and recent hospitalization for multidrug-resistant Klebsiella pneumoniae pneumonia. Initial imaging with contrast-enhanced computed tomography revealed an aneurysmatic dilatation of the right IIA, indicative of rupture. An endovascular repair was performed, employing a combination of stent grafts to achieve proximal and distal sealing and to restore vascular continuity. Outcome: The patient exhibited hemodynamic stability throughout the perioperative period and was transferred to the general ward postoperatively. However, he suffered a recurrent rupture on the 30th postoperative day, prompting a second endovascular intervention to extend the graft landing zone into the common iliac artery. Intraoperative findings confirmed localized plaque rupture as the underlying trigger for the initial vessel rupture. He ultimately achieved clinical stability and was discharged on the 35th postoperative day. Discussion: This case illustrates the critical importance of recognizing spontaneous IIA rupture as a potential complication in elderly patients, particularly in the context of recent severe infections. While the relationship between the rupture and the Klebsiella pneumoniae infection remains speculative, this report underscores the necessity of further research into the role of infectious processes in vascular integrity and susceptibility to rupture. Conclusions: The successful management of this rare and complex vascular emergency using endovascular techniques underscores the evolving landscape of minimally invasive interventions. This case contributes to the limited existing literature on spontaneous IIA rupture and highlights the need for increased clinical vigilance regarding atypical presentations in similar patient populations. Full article
Show Figures

Figure 1

Figure 1
<p>Multiplanar reformation (MPR view in axial (<b>A</b>), coronal (<b>B</b>), sagittal (<b>C</b>)) and 3D reconstruction (<b>D</b>) of preoperative CT angiography, showing right internal iliac artery rupture (highlighted with arrows).</p>
Full article ">Figure 2
<p>Multiplanar reformation (MPR view in axial (<b>A</b>), coronal (<b>B</b>), sagittal (<b>C</b>)) and 3D reconstruction (<b>D</b>) of CT angiography demonstrating leakage from the right internal iliac artery rupture site due to a type Ia endoleak (highlighted with arrows).</p>
Full article ">Figure 3
<p>Multiplanar reformation (MPR view in axial (<b>A</b>), coronal (<b>B</b>), sagittal (<b>C</b>)) and 3D reconstruction (<b>D</b>) of postoperative CT angiography demonstrating that the endograft (Endurant II limb) extends to cover the common and external iliac arteries, along with embolization of the right internal iliac artery.</p>
Full article ">Figure 4
<p>Abdominal CT scan performed one month prior to the rupture event showed no evidence of aneurysms.</p>
Full article ">
18 pages, 2085 KiB  
Article
Touching People with Gods: Droughts and Ritual Prayers in Southeastern China During the Eighth and Ninth Centuries
by Zejie Lin and Yanli Xie
Religions 2025, 16(3), 332; https://doi.org/10.3390/rel16030332 - 6 Mar 2025
Viewed by 147
Abstract
Between the eighth and ninth centuries, the world entered a second period of strong winter monsoons, which precipitated a series of recurrent natural disasters, including reduced summer rainfall and prolonged droughts. The various types of droughts that occurred in southeastern China are documented [...] Read more.
Between the eighth and ninth centuries, the world entered a second period of strong winter monsoons, which precipitated a series of recurrent natural disasters, including reduced summer rainfall and prolonged droughts. The various types of droughts that occurred in southeastern China are documented in historical records, which also include the official-led ritual prayers to the local deities that were conducted during these challenging periods. As evidenced in these historical records, officials implemented a series of measures to provide solace to the populace, including the restoration of shrines and temples and the offering of sacrifices and prayers to the local deities, such as the Wutang God 吳塘神 and the Chutan God 儲潭神. These actions were intended to leverage the influence of the local deities to mobilise labour and financial resources for the implementation of public works, including the reclamation of barren land and the construction of dikes and ponds. These initiatives ultimately proved instrumental in enabling the populace to withstand the adverse effects of disasters. This approach represents a distinctive strategy for coping with drought in ancient China. It may provide insights into how governments and non-governmental organisations can utilise the influence of religious beliefs to unite people in addressing the climate crisis in the present era. Full article
(This article belongs to the Special Issue Climate Crisis and Religions/Spirituality)
Show Figures

Figure 1

Figure 1
<p>A map of China during the Tang Dynasty.</p>
Full article ">Figure 2
<p>Drought outbreaks in the southeastern part of the Tang Dynasty, 7th–9th centuries.<a href="#fn013-religions-16-00332" class="html-fn">13</a></p>
Full article ">
20 pages, 9603 KiB  
Article
Improving Traditional Metrics: A Hybrid Framework for Assessing the Ecological Carrying Capacity of Mountainous Regions
by Rui Luo, Jiwei Leng, Daming He, Yanbo Li, Kai Ma, Ziyue Xu, Kaiwen Zhang and Yun Luo
Land 2025, 14(3), 549; https://doi.org/10.3390/land14030549 - 5 Mar 2025
Viewed by 221
Abstract
Ecological carrying capacity (ECC) is a crucial indicator for assessing sustainable development capabilities. However, mountain ecosystems possess unique complexities due to their diverse topography, high biodiversity, and fragile ecological environments. Addressing the current shortcomings in mountain ECC assessments, this paper proposes a novel [...] Read more.
Ecological carrying capacity (ECC) is a crucial indicator for assessing sustainable development capabilities. However, mountain ecosystems possess unique complexities due to their diverse topography, high biodiversity, and fragile ecological environments. Addressing the current shortcomings in mountain ECC assessments, this paper proposes a novel hybrid evaluation framework that integrates improved ecological footprint (EF) and ecosystem service value (ESV) approaches with spatial econometric models. This framework allows for a more comprehensive understanding of the dynamic changes and driving factors of the mountain ecological carrying capacity index (ECCI), using Pingbian County as a case study. The results indicate the following: (1) Land use changes and biodiversity exert varying impacts on the ECCI across different regions. The ECCI decreased by 42% from 2003 to 2021 (from 4.41 to 2.54), exhibiting significant spatial autocorrelation and heterogeneity. (2) The ecological service value coefficient is the main factor increasing the ECCI, while the energy consumption value and per capita consumption value inhibited the increase in the ECCI. For every 1% increase in the ecosystem service value coefficient, the ECCI increased by 0.66%, whereas every 1% increase in energy consumption value and per capita consumption value reduced the ECCI by 0.18% and 0.28%, respectively. (3) The overall spatial distribution pattern of the ECCI is primarily “southwest to northeast”, with the distance of centroid migration expanding over time. Based on these key findings, implementing differentiated land use practices and ecological restoration measures can effectively enhance the mountain ECCI, providing scientific support for the sustainable management of mountain areas. Full article
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Location and Topography of Pingbian County in Yunnan Province, Southwest China.</p>
Full article ">Figure 2
<p>Theoretical framework applied in the present analysis.</p>
Full article ">Figure 3
<p>Assessing model for ecological carrying capacity in mountainous areas.</p>
Full article ">Figure 4
<p>Land use/land cover (LULC) and biodiversity change in Pingbian County in 2003, 2013, and 2021.</p>
Full article ">Figure 5
<p>Spatial distribution of the ECCI from 2003 to 2021 in Pingbian County.</p>
Full article ">Figure 6
<p>LISA cluster of the ECCI of 98 villages in Pingbian County from 2003–2021.</p>
Full article ">Figure 7
<p>Standard deviational ellipses of the ECCI, center of gravity and driving factors in Pingbian County from 2003 to 2021.</p>
Full article ">Figure 8
<p>The consistency of the ecosystem service value (<b>a</b>), ecological footprint value (<b>b</b>), the ECCI (<b>c</b>), and the water yield (<b>d</b>) result.</p>
Full article ">
21 pages, 19423 KiB  
Article
Analysis of Landscape Fragmentation Evolution Characteristics and Driving Factors in the Wei River Basin, China
by Changzheng Gao, Qisen Dang, Chu Li and Yongming Fan
Land 2025, 14(3), 538; https://doi.org/10.3390/land14030538 - 4 Mar 2025
Viewed by 222
Abstract
Historically, the Wei River has served as part of the Yongji Canal section of the Grand Canal, playing a crucial role in connecting northern and southern China. However, with the acceleration of urbanization in China, issues such as excessive land development and ecological [...] Read more.
Historically, the Wei River has served as part of the Yongji Canal section of the Grand Canal, playing a crucial role in connecting northern and southern China. However, with the acceleration of urbanization in China, issues such as excessive land development and ecological landscape fragmentation have emerged. Exploring the mechanisms of landscape fragmentation evolution in the Wei River basin and proposing optimization strategies is of significant importance for land use and ecological stability within small- to medium-sized river basins. This study selected land use data from the Weihe River basin between 2000 and 2020, using landscape pattern indices to analyze the trend of landscape fragmentation. The principal component analysis (PCA) and geographical detector methods were employed to explore the distribution characteristics and driving factors of landscape fragmentation. The research results indicate that: (1) The degree of landscape fragmentation in the Wei River basin has progressively intensified over time. The edge density index (ED), the landscape division index (DIVISION), the landscape shape index (LSI), and the Shannon diversity index (SHDI) have increased annually, while the contagion index (CONTAG) and area-weighted mean patch size (Area_AM) have continuously decreased; (2) Landscape fragmentation in the Wei River basin is characterized by stable changes in the source and tributary fragmentation areas, a concentrated distribution of fragmentation in the tributaries, and a significant increase in fragmentation in the main stream; (3) The analysis using the geographic detector method indicates that vegetation coverage (FVC), human activity intensity (HAI), and land use/land cover change (LUCC) are the main driving factors of landscape fragmentation in the Wei River basin. The findings explore the mechanisms of landscape fragmentation in the basin and provide a reference for land use planning and ecological restoration in the region. Full article
Show Figures

Figure 1

Figure 1
<p>Study area of the Wei River basin.</p>
Full article ">Figure 2
<p>Division of independent variables in the geographic detector.</p>
Full article ">Figure 3
<p>Land use type distribution map of the Wei River basin. (<b>a</b>–<b>c</b>) represent the land use data for the Wei River Basin in 2000, 2010, and 2020, respectively. Note: The percentages represent the proportion of each land use type’s area relative to the total area of the basin.</p>
Full article ">Figure 4
<p>Changes in the land type index of the Wei River basin from 2000 to 2020. (<b>a</b>) trend of the ED index for each land use type, (<b>b</b>) trend of the LSI index for each land use type, (<b>c</b>) trend of the Area_AM index for each land use type, and (<b>d</b>) trend of the DIVISION index for each land use type.</p>
Full article ">Figure 5
<p>Spatial distribution maps of ED, LSI, and Area_AM in the Wei River basin. (<b>a</b>–<b>c</b>) represent the county-level spatial distribution of landscape pattern indices in the Wei River Basin for 2000, 2010, and 2020, respectively.</p>
Full article ">Figure 6
<p>Spatial distribution maps of CONTAG, DIVISION, and SHDI in the Wei River basin. (<b>a</b>–<b>c</b>) represent the county-level spatial distribution of landscape pattern indices in the Wei River Basin for 2000, 2010, and 2020, respectively.</p>
Full article ">Figure 7
<p>Spatiotemporal distribution pattern of comprehensive landscape fragmentation in the Wei River basin from 2000 to 2020. (<b>a</b>–<b>c</b>) represent the spatial distribution of comprehensive landscape fragmentation in the Wei River Basin for 2000, 2010, and 2020, respectively.</p>
Full article ">Figure 8
<p>Spatial distribution map of hotspots of comprehensive landscape fragmentation in the Wei River basin from 2000 to 2020. (<b>a</b>–<b>c</b>) represent the concentrated areas of moderate and severe comprehensive landscape fragmentation in the Wei River Basin for 2000, 2010, and 2020, respectively.</p>
Full article ">Figure 9
<p>Spatiotemporal distribution pattern of landscape fragmentation in each sub-basin of the Wei River from 2010 to 2020. (<b>a</b>–<b>c</b>) represent the spatial distribution of moderate and severe comprehensive landscape fragmentation in the headwaters, tributaries, and main stream of the Wei River Basin for 2000, 2010, and 2020, respectively.</p>
Full article ">Figure 10
<p>Optimal parameter discretization results of OPGD. Note: Digital Elevation Model (X1), Fractional Vegetation Cover (X2), Normalized Difference Vegetation Index (X3), Average Annual Precipitation (X4), Average Annual Temperature (X5), Annual Average Evaporation (X6), Human Activity Intensity (X7), Road Density (X8), Population Density (X9), Nighttime Lights (X10), and Land Use Classification (X11).</p>
Full article ">Figure 11
<p>Single-factor detection of the geographic detector in the Wei River basin. (<b>a</b>) represents the factor detector results for the driving factors: Digital Elevation Model (X1), Fractional Vegetation Cover (X2), Normalized Difference Vegetation Index (X3), Average Annual Precipitation (X4), Average Annual Temperature (X5), and Annual Average Evaporation (X6). (<b>b</b>) represents the factor detector results for the driving factors: Human Activity Intensity (X7), Road Density (X8), Population Density (X9), Nighttime Lights (X10), and Land Use Classification (X11).</p>
Full article ">Figure 12
<p>Interaction detection results of the geographic detector in the Wei River basin. Note: Digital Elevation Model (X1), Fractional Vegetation Cover (X2), Normalized Difference Vegetation Index (X3), Average Annual Precipitation (X4), Average Annual Temperature (X5), Annual Average Evaporation (X6), Human Activity Intensity (X7), Road Density (X8), Population Density (X9), Nighttime Lights (X10), and Land Use Classification (X11).</p>
Full article ">Figure 13
<p>Interaction detection types of major driving factors. Note: Digital Elevation Model (X1), Fractional Vegetation Cover (X2), Normalized Difference Vegetation Index (X3), Average Annual Precipitation (X4), Average Annual Temperature (X5), Annual Average Evaporation (X6), Human Activity Intensity (X7), Road Density (X8), Population Density (X9), Nighttime Lights (X10), and Land Use Classification (X11).</p>
Full article ">
22 pages, 3827 KiB  
Article
Species Richness of Arbuscular Mycorrhizal Fungi in Heterogenous Saline Environments
by Jahangir A. Malik, Basharat A. Dar, Abdulaziz A. Alqarawi, Abdulaziz M. Assaeed, Fahad Alotaibi, Arafat Alkhasha, Abdelmalik M. Adam and Ahmed M. Abd-ElGawad
Diversity 2025, 17(3), 183; https://doi.org/10.3390/d17030183 - 4 Mar 2025
Viewed by 202
Abstract
Sabkha (inland and coastal—saline beds or saline lands) are widespread in Saudi Arabia and are distinguished by their hypersaline nature. These hypersaline habitats are commonly covered by halophytic vegetation. Moreover, Arbuscular mycorrhizal fungi (AMF) are an essential component of these habitats and exhibit [...] Read more.
Sabkha (inland and coastal—saline beds or saline lands) are widespread in Saudi Arabia and are distinguished by their hypersaline nature. These hypersaline habitats are commonly covered by halophytic vegetation. Moreover, Arbuscular mycorrhizal fungi (AMF) are an essential component of these habitats and exhibit a unique adaptation and contribute significantly to ecosystem variability, diversity, and function. Additionally, AMF from saline habitats are an essential component for the successful rehabilitation of salinity-affected areas. Despite their importance, little is known about the distribution and abundance of AMF along inland and coastal sabkhat of Saudi Arabia. Therefore, the main objective of this study was to investigate the abundance and diversity of AMF in the coastal and inland sabkhat of Saudi Arabia. Five soil samples, each from five randomly selected spots (considering the presence of dominant and co-dominant halophytic species), were collected from every location and were used to assess the AMF abundance and diversity. The study indicated that the highest number of AMF spores was recorded from Jouf, averaging ≈ 346 spores 100 g−1 dry soil, and the lowest from Uqair, averaging ≈ 96 spores 100 g−1 dry soil. A total of 25 AMF species were identified, belonging to eight identified genera viz., Acaulospora, Diversispora, Gigaspora, Scutellospora, Claroideoglomus, Funneliformis, Glomus, and Rhizophagus and five families. Of the total identified species, 52% belonged to the family Glomeraceae. Moreover, the highest number of species was isolated from the sabkha in Qasab. Additionally, Glomeraceae was abundant in all the studied locations with the highest relative abundance in Uqair (48.34%). AMF species Claroideoglomus etunicatum, Funneliformis mosseae, Glomus ambisporum, and Rhizophagus intraradices were the most frequently isolated species from all the Sabkha locations with isolation frequency (IF) ≥ 60%, and Claroideoglomus etunicatum (Ivi ≥ 50%) was the dominant species in all the studied locations. Furthermore, data on the Shannon–Wiener diversity index showed that the highest AMF species diversity was in Qaseem and Qasab habitats. The highest Pielou’s evenness index was recorded in Jouf. Moreover, the soil parameters that positively affected the diversity of identified species included Clay%, Silt%, HCO31−, OM, MC, N, and P, while some soil parameters such as EC, Na+, SO42−, and Sand% had a significant negative correlation with the isolated AMF species. This study revealed that AMF can adapt and survive the harshest environments, such as hypersaline sabkhas, and thus can prove to be a vital component in the potential restoration of salinity-inflicted/degraded ecosystems. Full article
(This article belongs to the Special Issue Microbial Community Dynamics in Soil Ecosystems)
Show Figures

Figure 1

Figure 1
<p>Map of Saudi Arabia showing the different Sabkha locations (marked as red) assessed for investigating AMF abundance and diversity. Arabic terms denote the names of the different cities as: الرياض = Riyadh; المدينة المنورة = Medina; جدة = Jeddah; مكة المكرمة = Makkah; دبي = Dubai; مسقط = Muscat; صنعاء = Sana’a; دمشق = Damascus.</p>
Full article ">Figure 2
<p>AMF spore density in the samples collected from different inland and coastal sabkha locations around Saudi Arabia. The colored bars represent mean values (<span class="html-italic">n</span> = 5), while the error bars indicate the standard error (SE). Different letters above the error bars represent significant difference (<span class="html-italic">p</span> = 0.05) based on Tukey’s test. <span class="html-italic">*** p</span> &lt; 0.0001 (Tukey test).</p>
Full article ">Figure 3
<p>Relative abundance of AMF communities at order (<b>A</b>), and family (<b>B</b>) level in the soil samples collected from different sabkha habitats.</p>
Full article ">Figure 4
<p>Relative abundance of AMF communities at genus (<b>A</b>) and species (<b>B</b>) level in the soil samples collected from different sabkha habitats.</p>
Full article ">Figure 5
<p>The variation in AMF species among different hypersaline sabkha habitats with the Shannon–Wiener diversity index (<b>A</b>); Simpson’s dominance index (<b>B</b>); and Pielou’s evenness index (<b>C</b>) of species. Different letters above the error bars represent significant differences (<span class="html-italic">p</span> = 0.05) based on Tukey’s test. <span class="html-italic">* p</span> &lt; 0.01.</p>
Full article ">Figure 6
<p>The similarity index of AMF species between different hypersaline sabkha habitats.</p>
Full article ">Figure 7
<p>A correlation heatmap of the relationship between soil parameters and the AMF species isolated along different sabkha habitats. Red colors indicate a strong positive correlation while blue indicates a significant negative correlation between species and soil parameters.</p>
Full article ">Figure 8
<p>Principal component analysis (PCA) plot showing the associations between soil physiochemical parameters and AMF species along different sabkha locations.</p>
Full article ">
29 pages, 27723 KiB  
Article
A Geospatial Analysis Approach to Investigate Effects of Wildfires on Vegetation, Hydrological Response, and Recovery Trajectories in a Mediterranean Watershed
by Konstantinos Soulis, Stergia Palli Gravani, Rigas Giovos, Evangelos Dosiadis and Dionissios Kalivas
Hydrology 2025, 12(3), 47; https://doi.org/10.3390/hydrology12030047 - 4 Mar 2025
Viewed by 210
Abstract
Wildfires are frequently observed in watersheds with a Mediterranean climate and seriously affect vegetation, soil, hydrology, and ecosystems as they cause abrupt changes in land cover. Assessing wildfire effects, as well as the recovery process, is critical for mitigating their impacts. This paper [...] Read more.
Wildfires are frequently observed in watersheds with a Mediterranean climate and seriously affect vegetation, soil, hydrology, and ecosystems as they cause abrupt changes in land cover. Assessing wildfire effects, as well as the recovery process, is critical for mitigating their impacts. This paper presents a geospatial analysis approach that enables the investigation of wildfire effects on vegetation, soil, and hydrology. The prediction of regeneration potential and the period needed for the restoration of hydrological behavior to pre-fire conditions is also presented. To this end, the catastrophic wildfire that occurred in August 2021 in the wider area of Varybobi, north of Athens, Greece, is used as an example. First, an analysis of the extent and severity of the fire and its effect on the vegetation of the area is conducted using satellite imagery. The history of fires in the specific area is then analyzed using remote sensing data and a regrowth model is developed. The effect on the hydrological behavior of the affected area was then systematically analyzed. The analysis is conducted in a spatially distributed form in order to delineate the critical areas in which immediate interventions are required for the rapid restoration of the hydrological behavior of the basin. The period required for the restoration of the hydrological response is then estimated based on the developed vegetation regrowth models. Curve Numbers and post-fire runoff response estimations were found to be quite similar to those derived from measured data. This alignment shows that the SCS-CN method effectively reflects post-fire runoff conditions in this Mediterranean watershed, which supports its use in assessing hydrological changes in wildfire-affected areas. The results of the proposed approach can provide important data for the restoration and protection of wildfire-affected areas. Full article
(This article belongs to the Section Hydrological and Hydrodynamic Processes and Modelling)
Show Figures

Figure 1

Figure 1
<p>Geographic location of the burn scars created by the 2021 Varybobi wildfire and the adjacent watersheds. The above layers’ creation is described in the methodology section of the present study.</p>
Full article ">Figure 2
<p>Flowchart outlining the proposed methodology for the analysis of wildfires hydrological impact and recovery process.</p>
Full article ">Figure 3
<p>The CN–Rainfall data of the studied watershed and the fitted lines describing this relationship according to the Two-CN method [<a href="#B14-hydrology-12-00047" class="html-bibr">14</a>] and the Asymptotic CN [<a href="#B85-hydrology-12-00047" class="html-bibr">85</a>]. The corresponding CN values and the areas they cover are also shown.</p>
Full article ">Figure 4
<p>Variables used for the implementation of the model: (<b>a</b>) slope, (<b>b</b>) precipitation, (<b>c</b>) NDVI-produced 1-year vegetation regeneration, (<b>d</b>) TPI index, (<b>e</b>) dNBR index, and (<b>f</b>) model’s final regeneration prediction for the year 2031.</p>
Full article ">Figure 5
<p>Diachronic evolution of the NDVI index at the sites of the 1986 (red) and 1987 (blue) wildfires.</p>
Full article ">Figure 6
<p>NDVI difference between the pre-fire values (2021) and the 10-year regeneration prediction (2031).</p>
Full article ">Figure 7
<p>Diachronic evolution of soil–land use complexes, based on CLC data.</p>
Full article ">Figure 8
<p>Pre-fire CN ranges in the watersheds studied in the CLC reference years.</p>
Full article ">Figure 9
<p>Post-fire CN ranges in the study area after the implementation of the two methods on the 2018 CLC reference year; (<b>a</b>) 5, 10, 15, and 20 unit increases in the runoff CN value according to the burn severity classes [<a href="#B80-hydrology-12-00047" class="html-bibr">80</a>], and (<b>b</b>) post-fire CN values according to [<a href="#B28-hydrology-12-00047" class="html-bibr">28</a>].</p>
Full article ">Figure 10
<p>Direct runoff (mm) for the three return periods (5, 50, and 1000 years) estimated for the 2018 CLC reference year pre-fire and post-fire using two methods.</p>
Full article ">Figure 11
<p>Graphical illustration of runoff volume (mm) of the three study sub-areas for return periods of 5, 50, and 1000 years, respectively (<b>a</b>–<b>c</b>).</p>
Full article ">Figure 12
<p>Direct runoff values estimated with the post-fire CNs obtained by the two examined methods (Est. Direct Runoff—1 and 2 are the direct runoff estimations with method 1 and 2, correspondingly) plotted in comparison with the observed direct runoff.</p>
Full article ">
21 pages, 8129 KiB  
Article
Plants Drive Microbial Biomass and Composition but Not Diversity to Promote Ecosystem Multifunctionality in Karst Vegetation Restoration
by Yunlong Sun, Shu Zhang, Yueming Liang, Xuan Yu and Fujing Pan
Microorganisms 2025, 13(3), 590; https://doi.org/10.3390/microorganisms13030590 - 4 Mar 2025
Viewed by 136
Abstract
Natural restoration has emerged as a prominent approach in recent decades for the rehabilitation of degraded ecosystems globally. However, the specific changes and underlying mechanisms by natural restoration that influence the multifunctionality of karst ecosystems remain poorly understood. In this study, soil, litter, [...] Read more.
Natural restoration has emerged as a prominent approach in recent decades for the rehabilitation of degraded ecosystems globally. However, the specific changes and underlying mechanisms by natural restoration that influence the multifunctionality of karst ecosystems remain poorly understood. In this study, soil, litter, and fine root samples were collected from four chronosequence stages of vegetation restoration—grassland (G), shrubland (SH), shrub-tree land (ST), and forest (F)—within a karst ecosystem in Southwestern China. The aim was to evaluate the impacts of vegetation restoration on ecosystem multifunctionality using an averaging approach. The results demonstrated that the indices of C-cycling functionality, N-cycling functionality, P-cycling functionality, and total ecosystem multifunctionality increased as vegetation restoration progressed, along with plant diversity. The structure of plant, bacterial, and fungal communities varied across different stages of vegetation restoration, exhibiting the highest microbial diversity indices in the SH stage. Additionally, the tightness and complexity of co-occurrence networks of bacteria and fungi increased with advancing vegetation restoration, and higher positive links were observed in fungi than bacteria. The four functional indices were significantly and positively correlated with increasing plant diversity, fine root and litter nutrient contents, fine root biomass, microbial biomass, fungal community, enzyme activities, and soil nutrient contents but not with bacterial and fungal diversities. Furthermore, Random Forest model results revealed that plants exerted a significantly greater influence on ecosystem multifunctionality compared to other factors. It is plausible that plants influence soil microbial biomass, fungal community and co-occurrence networks, enzyme activities, and nutrient levels through the input of root and litter nutrients rather than by altering microbial diversity to enhance karst ecosystem multifunctionality. Therefore, initiatives to increase plant diversity are beneficial for sustainable ecological restoration management in the karst regions of Southwestern China. Full article
(This article belongs to the Special Issue Soil Microbial Carbon/Nitrogen/Phosphorus Cycling)
Show Figures

Figure 1

Figure 1
<p>Map of the four stages of vegetation restoration in Guilin, Southwestern China.</p>
Full article ">Figure 2
<p>Soil, fine root, litter nutrient and enzyme activities across advancing vegetation restorations. C-cycling parameters: Root-C (<b>a</b>), C contents of fine root; Litter-C (<b>b</b>), C contents of litter; MBC (<b>c</b>), microbial biomass C; SOC (<b>d</b>), soil organic carbon; and βG (<b>e</b>), β-Glucosidase activity. N-cycling parameters: Root-N (<b>f</b>), N contents of fine root; Litter-N (<b>g</b>), N contents of litter; MBN (<b>h</b>), microbial biomass N; TN (<b>i</b>), soil total N; NH<sub>4</sub><sup>+</sup>-N (<b>j</b>), ammonium N; NO<sub>3</sub><sup>−</sup>-N (<b>p</b>), nitrate N; NAG (<b>q</b>), β-1,4-N-acetylglucosaminidase activity; and LAP (<b>r</b>), leucine aminopeptidase activity. P-cycling parameters: Root-P (<b>k</b>), P contents of fine root; Litter-P (<b>l</b>), P contents of litter; MBP (<b>m</b>), microbial biomass P; TP (<b>n</b>), soil total P; AP (<b>o</b>), soil available P; ACP (<b>s</b>), acid phosphatase; ALP (<b>t</b>), alkaline phosphatase; and grassland (G), shrubland (SH), shrub-tree land (ST), and forest (F). Different letters mean significant differences (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 3
<p>The patterns of C-cycling functional (<b>a</b>), N-cycling functional (<b>b</b>), P-cycling functional (<b>c</b>), and total multifunctionality (<b>d</b>) indices across advancing vegetation restorations. Different letters mean significant differences (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 4
<p>The diversity indices of plants, bacteria, and fungi across advancing vegetation restorations. Plant Shannon (<b>a</b>), the Shannon–Wiener index of plants; Plant Simpson (<b>b</b>), the Simpson index of plants; Plant Pielou (<b>c</b>), the Pielou index of plants; bacterial Shannon (<b>d</b>), the Shannon–Wiener index of bacteria; bacterial Simpson (<b>e</b>), the Simpson index of bacteria; bacterial OTUs (<b>f</b>); bacterial Chao1 (<b>g</b>); fungal Shannon (<b>h</b>), the Shannon–Wiener index of fungi; and fungal Simpson (<b>i</b>), the Simpson index of fungi; fungi OTUs (<b>j</b>); fungi Chao1 (<b>k</b>). Different letters mean significant differences (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 5
<p>Community structures of plants, bacteria, and fungi across advancing vegetation restorations.</p>
Full article ">Figure 6
<p>Relative abundances at genus level of plants (<b>a</b>), bacteria (<b>b</b>), and fungi (<b>c</b>) across advancing vegetation restorations.</p>
Full article ">Figure 7
<p>Co-occurrence network models of bacteria (<b>a</b>) and fungi (<b>b</b>) at order level across advancing vegetation restorations. The red line indicates positive relation, and the green line indicates negative relation.</p>
Full article ">Figure 8
<p>Ecosystem multifunctionality indices related to plant, microbial, and soil factors. C-cycling, C-cycling functional index; N-cycling, N-cycling functional index; P-cycling, P-cycling functional index; Total, total multifunctionality index. Plant Shannon, Shannon–Wiener index of plants; Plant Simpson, Simpson index of plants; Plant Pielou, Pielou index of plants; bacterial Shannon, Shannon–Wiener index of bacteria; bacterial Simpson, Simpson index of bacteria; fungal Shannon, Shannon–Wiener index of fungi; and fungal Simpson, Simpson index of fungi. Root-C, C contents of fine root; Litter-C, C contents of litter; MBC, microbial biomass C; SOC, soil organic carbon; and βG, β-Glucosidase activity. Root-N, N contents of fine root; Litter-N, N contents of litter; MBN, microbial biomass N; TN, soil total N; NH<sub>4</sub><sup>+</sup>-N, ammonium N; NO<sub>3</sub><sup>−</sup>-N, nitrate N; NAG, β-1,4-N-acetylglucosaminidase activity; and LAP, leucine aminopeptidase activity. Root-P, P contents of fine root; Litter-P, P contents of litter; MBP, microbial biomass P; TP, soil total P; AP, soil available P; ACP, acid phosphatase; and ALP, alkaline phosphatase. ** <span class="html-italic">p</span> &lt; 0.01; * <span class="html-italic">p</span> &lt; 0.05.</p>
Full article ">Figure 9
<p>The changes in C-cycling functional (<b>a</b>), N-cycling functional (<b>b</b>), P-cycling functional (<b>c</b>), and total multifunctionality (<b>d</b>) indices are importantly ranked by plant, microbial, and soil factors. MSE is the mean square error, and the percentage of variations in MSE is used to estimate the relative importance of the measured variables. Green indicates the significant explanatory variables, while yellow denotes the non-significant explanatory variables. ** <span class="html-italic">p</span> &lt; 0.01; * <span class="html-italic">p</span> &lt; 0.05.</p>
Full article ">Figure 10
<p>Structural equation model results show that the influence path on soil C-cycling functional (<b>a</b>), N-cycling functional (<b>b</b>), P-cycling functional (<b>c</b>), and total multifunctional (<b>d</b>) indices. The parameters of these models: (<b>a</b>) X<sub>2</sub> = 1.741, degrees of freedom = 3, n = 19, CFI = 0.977, AGFI = 0.724, <span class="html-italic">p</span> = 0.628, RMSEA = 0.000; (<b>b</b>) X<sub>2</sub> = 1.741, degrees of freedom = 3, n = 19, CFI = 0.977, AGFI = 0.724, <span class="html-italic">p</span> = 0.628, RMSEA = 0.000; (<b>c</b>) X<sub>2</sub> = 1.741, degrees of freedom = 3, n = 19, CFI = 0.977, AGFI = 0.724, <span class="html-italic">p</span> = 0.628, RMSEA = 0.000; and (<b>d</b>) X<sub>2</sub> = 1.798, degrees of freedom = 4, n = 19, CFI = 0.976, AGFI = 0.786, <span class="html-italic">p</span> = 0.773, RMSEA = 0.000. Blue represents negative impact, red represents positive impact. ---, <span class="html-italic">p</span> ≥ 0.05, * <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.</p>
Full article ">
30 pages, 5634 KiB  
Article
Evaluating Ecosystem Service Trade-Offs and Recovery Dynamics in Response to Urban Expansion: Implications for Sustainable Management Strategies
by Mohammed J. Alshayeb
Sustainability 2025, 17(5), 2194; https://doi.org/10.3390/su17052194 - 3 Mar 2025
Viewed by 239
Abstract
Land use land cover (LULC) changes due to rapid urbanization pose critical challenges to sustainable development, particularly in arid and semi-arid regions like Saudi Arabia, where cities such as Abha are experiencing unprecedented expansion. Urban sprawl is accelerating environmental degradation, affecting key natural [...] Read more.
Land use land cover (LULC) changes due to rapid urbanization pose critical challenges to sustainable development, particularly in arid and semi-arid regions like Saudi Arabia, where cities such as Abha are experiencing unprecedented expansion. Urban sprawl is accelerating environmental degradation, affecting key natural resources such as vegetation, water bodies, and barren land. This study introduces an advanced machine learning (ML) and deep learning (DL)-based framework for high-accuracy LULC classification, urban sprawl quantification, and ecosystem service assessment, providing a more precise and scalable approach compared to traditional remote sensing techniques. A hybrid methodology combining ML models—Random Forest, Artificial Neural Networks, Gradient Boosting Machine, and LightGBM—with a 1D Convolutional Neural Network (CNN) was fine-tuned using grid search optimization to enhance classification accuracy. The integration of deep learning improves feature extraction and classification consistency, achieving an AUC of 0.93 for Dense Vegetation and 0.82 for Cropland, outperforming conventional classification methods. The study also applies the Markov transition model to project land cover changes, offering a probabilistic understanding of urban expansion trends and ecosystem dynamics, providing a significant improvement over static LULC assessments by quantifying transition probabilities and predicting future land cover transformations. The results reveal that urban areas in Abha expanded by 120.74 km2 between 2014 and 2023, with barren land decreasing by 557.09 km2 and cropland increasing by 205.14 km2. The peak ecosystem service value (ESV) loss was recorded at USD 125,662.7 between 2017 and 2020, but subsequent land management efforts improved ESV to USD 96,769.5 by 2023. The resilience and recovery of natural land cover types, particularly barren land (44,163 km2 recovered by 2023), indicate the potential for targeted restoration strategies. This study advances urban sustainability research by integrating state-of-the-art deep learning models with Markov-based land change predictions, enhancing the accuracy and predictive capability of LULC assessments. The findings highlight the need for proactive land management policies to mitigate the adverse effects of urban sprawl and promote sustainable ecosystem service recovery. The methodological advancements presented in this study provide a scalable and adaptable framework for future urbanization impact assessments, particularly in rapidly developing regions. Full article
Show Figures

Figure 1

Figure 1
<p>Study area.</p>
Full article ">Figure 2
<p>Training and validation loss curves for a 1D CNN model.</p>
Full article ">Figure 3
<p>Confusion matrices of ML and DL models for LULC classification evaluating RF, ANN, GBM, LightGBM, and 1D CNN models, highlighting classification accuracy and misclassification trends across land cover classes.</p>
Full article ">Figure 4
<p>ROC curves and AUC values for Random Forest, ANN, GBM, LightGBM, and 1D CNN models for six land cover classes.</p>
Full article ">Figure 5
<p>Spatiotemporal distribution of LULC classes for the years (<b>a</b>) 2014, (<b>b</b>) 2017, (<b>c</b>) 2020, and (<b>d</b>) 2023.</p>
Full article ">Figure 6
<p>Land cover area for different classes for the years 2014, 2017, 2020, and 2023.</p>
Full article ">Figure 7
<p>Probability-based Markov transition matrices depicting the dynamic land cover changes between 2014–2017, 2017–2020, 2020–2023, and overall, for 2014–2023, quantifying transformation trends among LULC categories.</p>
Full article ">Figure 8
<p>Temporal analysis (2014 to 2023) showing trends in urban growth metrics over time, including urban growth rate (<b>top left</b>), Shannon’s entropy (<b>top right</b>), urban fragmentation (<b>bottom left</b>), and urban edge growth (<b>bottom right</b>), highlighting spatial and structural changes in urban expansion.</p>
Full article ">
25 pages, 2715 KiB  
Article
Spatial and Temporal Pervasiveness of Indigenous Settlement in Oak Landscapes of Southern New England, US, During the Late Holocene
by Stephen J. Tulowiecki, Brice B. Hanberry and Marc D. Abrams
Land 2025, 14(3), 525; https://doi.org/10.3390/land14030525 - 3 Mar 2025
Viewed by 361
Abstract
The relative influence of climate and Indigenous cultural burning on past forest composition in southern New England, US, remains debated. Employing varied analyses, this study compared data on Indigenous settlements from over 5000 years before present (YBP) with relative tree abundances estimated from [...] Read more.
The relative influence of climate and Indigenous cultural burning on past forest composition in southern New England, US, remains debated. Employing varied analyses, this study compared data on Indigenous settlements from over 5000 years before present (YBP) with relative tree abundances estimated from pollen and land survey records. Results suggested that fire-tolerant vegetation, mainly oak (Quercus spp.), was more abundant near Indigenous settlements from 4955 to 205 YBP (i.e., 86–91% fire-tolerant trees), and significantly (p < 0.05) higher from 3205 to 205 YBP; fire-tolerant vegetation was less abundant away from settlements, where it also experienced greater fluctuations. Correlative models showed that warmer temperatures and distance to Indigenous settlement, which are both indicators of fire, were important predictors in the 17th–18th centuries of fire-tolerant tree abundance; soil variables were less important and their relationships with vegetation were unclear. A marked increase in oak abundance occurred above 8 °C mean annual temperature and within 16 km of major Indigenous settlements. Pyrophilic vegetation was most correlated with distance to Indigenous villages in areas with 7–9 °C mean annual temperature, typical of higher latitudes and elevations that usually supported northern hardwoods. Widespread burning in warmer areas potentially weakened relationships between distance and pyrophilic abundance. Indigenous land use imprinted upon warmer areas conducive to burning created patterns in fire-tolerant vegetation in southern New England, plausibly affecting most low-elevation areas. Results imply that restoration of fire-dependent species and of barrens, savannas, and woodlands of oak in southern New England benefit from cultural burning. Full article
Show Figures

Figure 1

Figure 1
<p>(<b>a</b>) Indigenous geography with 17th century settlement areas [<a href="#B49-land-14-00525" class="html-bibr">49</a>], 17th century villages [<a href="#B50-land-14-00525" class="html-bibr">50</a>], notable 16th–18th century archaeological sites [<a href="#B51-land-14-00525" class="html-bibr">51</a>], radiocarbon-dated archaeological sites [<a href="#B52-land-14-00525" class="html-bibr">52</a>], and 17th century major trails [<a href="#B50-land-14-00525" class="html-bibr">50</a>]. The same Indigenous site can appear in multiple layers. (<b>b</b>) Relative abundance of pyrophilic tree taxa circa 17th–18th centuries CE [<a href="#B45-land-14-00525" class="html-bibr">45</a>], charcoal from palynology sites, and mean annual temperature [<a href="#B53-land-14-00525" class="html-bibr">53</a>]. Charcoal records are scaled from 0 (lowest) to 1 (highest) for each dataset to create a common scale, because they are provided in different units: mean pre-European charcoal-to-pollen ratios [<a href="#B33-land-14-00525" class="html-bibr">33</a>,<a href="#B35-land-14-00525" class="html-bibr">35</a>] and mean number of charcoal pieces [<a href="#B30-land-14-00525" class="html-bibr">30</a>]. Time periods vary across charcoal sites, and some records include post-European charcoal [<a href="#B30-land-14-00525" class="html-bibr">30</a>].</p>
Full article ">Figure 2
<p>Oak relative abundance [<a href="#B71-land-14-00525" class="html-bibr">71</a>] from 2005 BCE to 1745 CE (3955–205 years before present [YBP]), and number of archaeological dates [<a href="#B52-land-14-00525" class="html-bibr">52</a>] from the preceding 250 yr. Abundance estimates did not exist for some coastal areas.</p>
Full article ">Figure 2 Cont.
<p>Oak relative abundance [<a href="#B71-land-14-00525" class="html-bibr">71</a>] from 2005 BCE to 1745 CE (3955–205 years before present [YBP]), and number of archaeological dates [<a href="#B52-land-14-00525" class="html-bibr">52</a>] from the preceding 250 yr. Abundance estimates did not exist for some coastal areas.</p>
Full article ">Figure 3
<p>(<b>a</b>) Oak (<span class="html-italic">Quercus</span> spp.) and (<b>b</b>) pyrophilic vegetation relative abundance from 3005 BCE to 1745 CE (4955–205 years before present), in archaeological site presence and absence locations at 24 km resolution. Non-significant differences are indicated with an asterisk on the <span class="html-italic">x</span>-axis labels.</p>
Full article ">
19 pages, 2422 KiB  
Article
Study on Coastline Protection Strategies in Guangdong Province, China
by Xiaohao Zhang, Huamei Huang, Jingrou Lin and Sumei Xie
Water 2025, 17(5), 727; https://doi.org/10.3390/w17050727 - 2 Mar 2025
Viewed by 259
Abstract
The length of the mainland coastline in Guangdong Province ranks first in the country, and the rapid development of the marine economy have also supported Guangdong Province’s GDP to remain at the top of the country for 35 consecutive years. The coastline has [...] Read more.
The length of the mainland coastline in Guangdong Province ranks first in the country, and the rapid development of the marine economy have also supported Guangdong Province’s GDP to remain at the top of the country for 35 consecutive years. The coastline has extremely important ecological functions and resource values. Guangdong Province has always attached great importance to the renovation and restoration of its coastline, continuously strengthening the ecological, disaster reduction, and tourism functions of the coastal areas. This article analyzes the main measures, achievements, and main problems of coastal protection in Guangdong Province and selects typical areas for driving force analysis. Finally, some thoughts and targeted countermeasures on the protection of Guangdong Province’s coastline are proposed, which provide useful references for comprehensively strengthening coastline protection, scientifically carrying out coastline renovation and restoration, and improving the natural coastline retention rate in the future. This can also output wisdom and experience for the construction of a maritime power under the background of land–sea coordination. Full article
Show Figures

Figure 1

Figure 1
<p>Map of the geographical scope of the study area.</p>
Full article ">Figure 2
<p>Distribution of mainland coastline lengths in various cities of Guangdong Province.</p>
Full article ">Figure 3
<p>Wind power and fishery breeding facilities near the coastline.</p>
Full article ">Figure 4
<p>Distribution map of reclamation areas in Shenzhen.(Blue represents the sea, white represents the land, and gray represents the land of Shenzhen).</p>
Full article ">Figure 5
<p>Sketch map of “eight lines” in coastal areas.</p>
Full article ">Figure 6
<p>Typical case of the distribution of ponds outside the coastline (the red line represents the coastline announced by the government).</p>
Full article ">
25 pages, 24262 KiB  
Article
Dynamic Load Balancing Based on Hypergraph Partitioning for Parallel Geospatial Cellular Automata Models
by Wei Xia, Qingfeng Guan, Yuanyuan Li, Hanqiu Yue, Xue Yang and Huan Gao
ISPRS Int. J. Geo-Inf. 2025, 14(3), 109; https://doi.org/10.3390/ijgi14030109 - 1 Mar 2025
Viewed by 383
Abstract
Parallel computing techniques have been adopted in geospatial cellular automata (CA) models to improve computational efficiency, enabling large-scale complex simulations of land use and land cover (LULC) changes at fine scales. However, the spatial distribution of computational intensity often changes along with the [...] Read more.
Parallel computing techniques have been adopted in geospatial cellular automata (CA) models to improve computational efficiency, enabling large-scale complex simulations of land use and land cover (LULC) changes at fine scales. However, the spatial distribution of computational intensity often changes along with the spatiotemporal dynamics of LULC during the simulation, leading to an increase in load imbalance among computing units and degradation of the computational performance of a parallel CA. This paper presents a dynamic load balancing method based on hypergraph partitioning for multi-process parallel geospatial CA models. During the simulation, the sub-domains are dynamically reassigned to computing processes through hypergraph partitioning according to the spatial variation in computational workloads to restore load balance. In addition, a novel mechanism called Migrated-SubCellspaces-First (MSCF) is proposed to reduce the cost of workload migration by employing a non-blocking communication technique to further improve computational performance. To demonstrate and evaluate the effectiveness of our method, a parallel geospatial CA model with hypergraph-based dynamic load balancing is developed. Experiments using a dataset from California showed that the proposed dynamic load balancing method achieved a computational performance enhancement of 62.59% by using 16 processes compared with a parallel CA with static load balancing. Full article
Show Figures

Figure 1

Figure 1
<p>An example of data parallelism for multilayer geospatial CA.</p>
Full article ">Figure 2
<p>Regular and irregular domain decomposition methods.</p>
Full article ">Figure 3
<p>Approaches for M-1 assignment.</p>
Full article ">Figure 4
<p>Two approaches for data I/O.</p>
Full article ">Figure 5
<p>Different types of cells and communications among computing units.</p>
Full article ">Figure 6
<p>The framework of hypergraph-based dynamic load balancing for a parallel CA.</p>
Full article ">Figure 7
<p>An example of sub-domain assignment by hypergraph partitioning; the darker color of the circle indicates higher computational intensity of the sub-domain.</p>
Full article ">Figure 8
<p>An example of an initial sub-cellspace assignment.</p>
Full article ">Figure 9
<p>Initial assignment by hypergraph partitioning. Twelve sub-cellspaces are divided into 3 groups (i.e., assignments for 3 processes). Sub-cellspaces are depicted as circles (darker color represents higher computational intensity and longer computing time), and communication costs are depicted as squares. Squares a, b, and c represent the communication costs among processes.</p>
Full article ">Figure 10
<p>(<b>a</b>) A sample of computational workloads becomes highly imbalanced at iteration k-1. (<b>b</b>) A solution of repartitioning hypergraph.</p>
Full article ">Figure 11
<p>An example of MSCF.</p>
Full article ">Figure 12
<p>Flowchart of logistic CA.</p>
Full article ">Figure 13
<p>A 50-year simulation of urban growth.</p>
Full article ">Figure 14
<p>Computing times of sLCA, pLCA, and dpLCA on different numbers of processes.</p>
Full article ">Figure 15
<p>RSD value of pLCA and dpLCA on different numbers of processes.</p>
Full article ">Figure 16
<p>Speedups of pLCA and dpLCA on different numbers of processes.</p>
Full article ">Figure 17
<p>Parallel efficiency of pLCA and dpLCA on different numbers of processes.</p>
Full article ">
20 pages, 4068 KiB  
Article
Land Reclamation in the Mississippi River Delta
by Glenn M. Suir, Christina Saltus and Jeffrey M. Corbino
Remote Sens. 2025, 17(5), 878; https://doi.org/10.3390/rs17050878 - 1 Mar 2025
Viewed by 267
Abstract
Driven by the need to expand urban/industrial complexes, and/or mitigate anticipated environmental impacts (e.g., tropical storms), many coastal countries have long implemented large-scale land reclamation initiatives. Some areas, like coastal Louisiana, USA, have relied heavily on restoration activities (i.e., beneficial use of dredged [...] Read more.
Driven by the need to expand urban/industrial complexes, and/or mitigate anticipated environmental impacts (e.g., tropical storms), many coastal countries have long implemented large-scale land reclamation initiatives. Some areas, like coastal Louisiana, USA, have relied heavily on restoration activities (i.e., beneficial use of dredged material) to counter extensive long-term wetland loss. Despite these prolonged engagements, the quantifiable benefits of these activities have lacked comprehensive documentation. Therefore, this study leveraged remote sensing data and advanced machine learning techniques to enhance the classification and evaluation of restoration efficacy within the wetlands adjacent to the Mississippi River’s Southwest Pass (SWP). By utilizing air- and space-borne imagery, land and water data were extracted and used to compare land cover changes during two distinct restoration periods (1978 to 2008 and 2008 to 2020) to historical trends. The classification methods employed achieved an overall accuracy of 85% with a Cohen’s kappa value of 0.82, demonstrating substantial agreement beyond random chance. To further assess the success of the SWP reclamation efforts in a global context, broad-based land cover data were generated using biennial air- and space-borne imagery. Results show that restoration activities along SWP have resulted in a significant recovery of degraded wetlands, accounting for approximately a 30 km2 increase in land area, ranking among the most successful land reclamation projects in the world. The findings from this study highlight beneficial use of dredged material as a critical component in large-scale, recurring restoration activities aimed at mitigating degradation in coastal landscapes. The integration of remote sensing and machine learning methodologies provides a robust framework for monitoring and evaluating restoration projects, offering valuable insights into the optimization of ecosystem services. Overall, the research advocates for a holistic approach to coastal restoration, emphasizing the need for continuous innovation and adaptation in restoration practices to address the dynamic challenges faced by coastal ecosystems globally. Full article
(This article belongs to the Special Issue Remote Sensing in Coastal Vegetation Monitoring)
Show Figures

Figure 1

Figure 1
<p>Location map of the Southwest Pass study area.</p>
Full article ">Figure 2
<p>Area and location of dredged material placement sites within the Southwest Pass study area. Early dredged material placement activity locations were not always documented (those listed as historical SWP O&amp;M).</p>
Full article ">Figure 3
<p>Total subaerial land and placement site area within the Southwest Pass study area from 1934 to 2020 for three time periods: historical 1934–1978, initial BUDM 1978–2008, and current reclamation 2008–2020.</p>
Full article ">Figure 4
<p>Land gain (greens and blues) and loss (oranges and reds) areas within the Southwest Pass study area from 1934 to 2020.</p>
Full article ">Figure 5
<p>List of the top coastal land reclamation projects using dredged sediment.</p>
Full article ">
Back to TopTop