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20 pages, 2381 KiB  
Article
Impact of Loblolly Pine (Pinus taeda L.) Plantation Management on Biomass, Carbon Sequestration Rates and Storage
by Farzam Tavankar, Rodolfo Picchio, Mehrdad Nikooy, Behroz Karamdost Marian, Rachele Venanzi and Angela Lo Monaco
Sustainability 2025, 17(3), 888; https://doi.org/10.3390/su17030888 - 22 Jan 2025
Abstract
Loblolly pine plantations have long been cultivated primarily for timber production due to their rapid growth and economic value. However, these forests are now increasingly acknowledged for their important role in mitigating climate change. Their dense canopies and fast growth rates enable them [...] Read more.
Loblolly pine plantations have long been cultivated primarily for timber production due to their rapid growth and economic value. However, these forests are now increasingly acknowledged for their important role in mitigating climate change. Their dense canopies and fast growth rates enable them to absorb and store substantial amounts of atmospheric carbon dioxide. By integrating sustainable management practices, these plantations can maximize both timber yield and carbon sequestration, contributing to global efforts to reduce greenhouse gas emissions. Balancing timber production with vital ecosystem services, such as carbon storage, demands carefully tailored management strategies. This study examined how the timing of thinning—specifically early thinning at 17 years and late thinning at 32 years—impacts biomass accumulation, carbon storage capacity, and carbon sequestration rates in loblolly pine plantations located in northern Iran. Two thinning intensities were evaluated: normal thinning (removal of 15% basal area) and heavy thinning (removal of 35% basal area). The results demonstrated that thinning significantly improved biomass, sequestration rates and carbon storage compared to unthinned stands. Early thinning proved more effective than late thinning in enhancing these metrics. Additionally, heavy thinning had a greater impact than normal thinning on increasing biomass, carbon storage, and sequestration rates. In early heavy-thinned stands, carbon storage reached 95.8 Mg C/ha, which was 63.0% higher than the 58.8 Mg C/ha observed in unthinned 32-year-old stands. In comparison, early normal thinning increased carbon storage by 41.3%. In late heavy-thinned stands, carbon storage reached 199.4 Mg C/ha, which was 29.0% higher than in unthinned stands of the same age (154.6 Mg C/ha at 52 years). In contrast, late normal thinning increased carbon storage by 13.3%. Similarly, carbon sequestration rates in unthinned stands were 1.84 Mg C/ha/yr at 32 years and 2.97 Mg C/ha/yr at 52 years. In comparison, 32-year-old stands subjected to normal and heavy thinning had sequestration rates of 2.60 and 2.99 Mg C/ha/yr, respectively, while 54-year-old normally and heavily thinned stands reached 3.37 and 3.83 Mg C/ha/yr, respectively. The highest carbon storage was concentrated in the stems for 52–58% of the total. Greater thinning intensity increased the proportion of carbon stored in stems while decreasing the contribution from foliage. These results indicate that heavy early thinning is the most effective strategy for maximizing both timber production and carbon sequestration in loblolly pine plantations. Full article
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<p>Effect of thinning intensity on carbon storage in individual tree components in early and late thinned stands. NT: Normal thinning, HT: Heavy thinning, UT-32: Unthinned at 32 years of age, UT-52: Unthinned at 52 years of age, AGC: Aboveground carbon, BGC: Belowground carbon, WTC: Whole tree carbon. Different letters indicate significant differences between thinned and unthinned stands, as determined by Duncan’s test at α = 0.05 for early and late thinned stands.</p>
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<p>Effect of thinning intensity at the stand level on carbon storage in stand components in early and late thinned stands. NT: Normal thinning, HT: Heavy thinning, UT-32: Unthinned at 32 years of age, UT-52: Unthinned at 52 years of age. AGC: Aboveground carbon, BGC: Belowground carbon, WTC: Whole tree carbon. Different letters indicate significant differences between thinned and unthinned stands, as determined by Duncan’s test at α = 0.05 for early and late thinned stands.</p>
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<p>Effect of the thinning on C content (%) of tree components in the loblolly pine plantations. NT: normal thinning, HT: heavy thinning, UT-32: unthinned at the age 32 years, UT-52: unthinned at the age 52 years, BGC: below ground carbon.</p>
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<p>Carbon sequestration rate (CSR) in the loblolly pine plantations by intensity and time of thinning. NT: normal thinning, HT: heavy thinning, UT-32: unthinned at the age 32 years, UT-52: unthinned at the age 52 years.</p>
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<p>Whole tree biomass (WTB) of individual tree (<b>A</b>), stand (<b>B</b>), and carbon sequestration rate (CSR) (<b>C</b>) in relation to tree density in the loblolly pine plantations.</p>
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21 pages, 6155 KiB  
Article
Impact of Anticyclonic Mesoscale Eddies on the Vertical Structures of Marine Heatwaves in the South China Sea
by Xindi Song, Ruili Sun, Shuangyan He, Haoyu Zhang, Yanzhen Gu, Peiliang Li and Jinbao Song
Remote Sens. 2025, 17(3), 370; https://doi.org/10.3390/rs17030370 - 22 Jan 2025
Abstract
Under global warming, the South China Sea (SCS) is experiencing increasingly severe marine heatwaves (MHWs), with impacts on marine ecosystems such as coral reefs and marine pastures becoming more evident. The numerous anticyclonic eddies (AEs) distributed in the SCS are important drivers of [...] Read more.
Under global warming, the South China Sea (SCS) is experiencing increasingly severe marine heatwaves (MHWs), with impacts on marine ecosystems such as coral reefs and marine pastures becoming more evident. The numerous anticyclonic eddies (AEs) distributed in the SCS are important drivers of MHW generation and development, yet their impacts on MHWs are still not fully understood. In this study, the vertical structures of various types of MHWs inside the AEs and in the background field were mapped and compared, and we found that AEs of varying amplitudes have distinct impacts on the vertical structures of MHWs. MHWs inside the AEs can be divided into two categories: subsurface-reversed MHWs and subsurface-intensified MHWs. The former is manifested as anomalous cooling in the subsurface, driven by the uplift of thermocline due to the inhibition of downward mixing. The latter is characterized by anomalous warming in the subsurface, resulting from strong vertical warm-water subsidence induced by large-amplitude AEs. This process may penetrate the thermocline and produce maximum warming anomalies in the layer beneath the region of greatest temperature gradient change. Our research reveals characteristics of various vertical structures of MHWs in the SCS, attributing their differences to the stable water layer’s different response to varying intensities of vertical heat conduction, and deepening people’s understanding of the impact of AEs in the SCS on the vertical structure of MHWs. Full article
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<p>Mesoscale eddies and marine heatwaves (MHWs) in the South China Sea (SCS). (<b>a</b>) Bathymetric topography overlaid with sea-level anomalies (SLAs) in the SCS (gray solid lines indicate positive values, gray dashed lines indicate negative values, with 3 cm intervals), along with preliminarily identified eddy boundaries (2020-1-1). Red solid lines represent anticyclonic eddies (AEs), while green solid lines represent cyclonic eddies (CEs) (the calculation of AEs and CEs is derived from SLA data by identifying closed contours and characterizing them using parameters such as the eddy center position and radius). XSI, ZSI, NSI, and DSI correspond to the Xisha, Zhongsha, Nansha, and Dongsha Islands. (<b>b</b>) Spatial distribution of MHW frequency in the SCS from 1993 to 2022.</p>
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<p>Vertical structure of MHWs in the SCS. (<b>a</b>) Spatial distribution of MHWs with corresponding vertical structures. (<b>b</b>) Minimum and (<b>c</b>) maximum temperature anomalies of vertical structures and their depths. Red dots mark MHWs inside the eddy, while blue dots mark MHWs located in the background field. The size of the dots in (<b>b</b>,<b>c</b>) marks the number of events, with the largest circle marking 33 events and the smallest circle marking 1 event.</p>
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<p>Vertical structure of composited MHWs (<b>a</b>) in the background field (BF-MHW) and (<b>b</b>) inside the AEs (AE-MHW) and (<b>c</b>) their difference (AE–BF). The gray dashed lines indicate the zero contour lines. The shadings represent the standard deviations of the vertical temperature anomalies.</p>
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<p>Composites of sea surface temperature anomalies (SSTAs) and ocean currents within 1° around MHWs (<b>a</b>) in the background field and (<b>b</b>) inside the AEs and (<b>c</b>) their difference.</p>
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<p>Composites of vertical structures for two types of MHWs inside the AEs and their surrounding SSTAs and ocean currents. (<b>a</b>) Vertical structure and (<b>d</b>) SSTAs and ocean current composites of subsurface-reversed MHWs; (<b>b</b>) vertical structure and (<b>e</b>) SSTAs and ocean current composites of subsurface-intensified MHWs; the difference in (<b>c</b>) vertical structure and (<b>f</b>) SSTAs and ocean current composites of two types of MHWs; SR-MHW, IR-MHW and SI–SR represent subsurface-reversed MHWs, subsurface-intensified MHWs, and the differences between them, respectively. The shadings and gray dashed lines in (<b>a</b>–<b>c</b>) represent the standard deviations of the vertical temperature anomalies and zeros, respectively. The colors in (<b>d</b>–<b>f</b>) represent the SSTAs (°C).</p>
Full article ">Figure 6
<p>Warming effect of different-amplitude AEs on the vertical structures of MHWs. Differences in the average vertical structures between (<b>a</b>) subsurface-reversed MHWs and background-field MHWs; (<b>b</b>) subsurface-intensified MHWs and background-field MHWs. BF-MHW, SR-MHW, IR-MHW, and SR(SI)–BF represent background-field MHWs, subsurface-reversed MHWs, subsurface-intensified MHWs, and their differences, respectively. Gray dashed lines indicate zeros. Shadings represent the standard deviations of the vertical temperature anomalies.</p>
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<p>Thermocline variations at the locations of different types of MHWs. (<b>a</b>) Thermocline anomalies at the location of each MHW. (<b>b</b>) Box plot of the thermocline uplift values (values for which the thermocline anomaly is less than zero) at the locations of different types of MHWs. BF-MHW, SR-MHW, and IR-MHW represent MHWs in the background field, subsurface-reversed MHWs, and subsurface-intensified MHWs, respectively. The box represents the interquartile range (IQR), containing 25% to 75% of the thermocline uplift values. The bottom and top edges of the box correspond to the first quartile (Q1) and third quartile (Q3), respectively. The line inside the box represents the median of the thermocline uplift. The whiskers extend to values 1.5 times the IQR beyond the box. The upper whisker extends to the maximum value within 1.5 × IQR above the box’s top edge (Q3), and the lower whisker extends to the minimum value within 1.5 × IQR below the box’s bottom edge (Q1). Dots beyond the whiskers represent outliers.</p>
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<p>The thermocline uplift under the influence of an MHW formed by a strong AE.</p>
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<p>Effects of AEs with different amplitudes (A) on the vertical structures of MHWs. The amplitudes falling below (<b>a</b>) 80%, (<b>b</b>) 50%, and (<b>c</b>) 20%, and exceeding (<b>d</b>) 20%, (<b>e</b>) 50%, and (<b>f</b>) 80%. The pink and orange dashed lines represent the vertical structures of MHWs in AEs of small and large amplitudes, respectively, the gray dashed line indicates the mean vertical structures of MHWs in the AEs, and the black solid line shows the difference between the vertical structures of MHWs in AEs of different amplitudes and the mean vertical structures of all MHWs; the blue dashed lines indicate zeros. Shadings represent the standard deviations of the vertical temperature anomalies.</p>
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<p>Correlation between the amplitudes of AEs and their maximum temperature anomalies and corresponding depths. (<b>a</b>) Correlation between the amplitudes of small AEs and their maximum cooling anomalies and corresponding depths, with the <span class="html-italic">x</span>-axis representing the percentiles below the threshold amplitude, the blue solid dots indicating the maximum cooling anomalies, and the light blue dashed boxes representing the depths of these anomalies. (<b>b</b>) Correlation between the amplitudes of large AEs and their maximum warming anomalies and corresponding depths, with the <span class="html-italic">x</span>-axis representing the percentiles above the threshold amplitude, and the red solid dots indicating the maximum warming anomalies and the light red dashed box representing the depths of these anomalies.</p>
Full article ">Figure A1
<p>SOM training results under 1 × 2 grid. The red lines represent the composites of vertical structures for different types of MHWs. The black dashed lines indicate zeros. The shadings represent the standard deviations of the vertical temperature anomalies.</p>
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<p>SOM training results under 2 × 2 grid. The red lines represent the composites of vertical structures for different types of MHWs. The black dashed lines indicate zeros. The shadings represent the standard deviations of the vertical temperature anomalies.</p>
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<p>SOM training results under 2 × 3 grid. The red lines represent the composites of vertical structures for different types of MHWs. The black dashed lines indicate zeros. The shadings represent the standard deviations of the vertical temperature anomalies.</p>
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26 pages, 1750 KiB  
Article
Understanding Imbalanced Transmission from R&D Inputs into Innovation Outputs and Impacts: Evidence from Kazakhstan
by Stefka Slavova, Luis Rubalcaba and José Nicanor Franco-Riquelme
Economies 2025, 13(2), 25; https://doi.org/10.3390/economies13020025 - 22 Jan 2025
Abstract
Innovation ecosystems use R&D inputs to generate innovation outputs first and innovation impacts later. But some countries show a relatively low transmission, such as in the case of Kazakhstan, the largest economy in Central Asia. This article analyzes the transmission from R&D into [...] Read more.
Innovation ecosystems use R&D inputs to generate innovation outputs first and innovation impacts later. But some countries show a relatively low transmission, such as in the case of Kazakhstan, the largest economy in Central Asia. This article analyzes the transmission from R&D into innovation outputs and impacts through a framework for which different factors matter, such as the company size, education and skills, competition, exports, and foreign ownership. Transmission is conceptually understood in two steps: from R&D into innovation outputs, and from innovation output into innovation impacts. The main hypothesis is that the high endowments of these company factors should lead to the better transmission of results and improved performance in terms of outputs and impacts. We test this using new evidence from Kazakhstan and the ECA region (Europe and Central as defined by the World Bank) as benchmarking, and data are from the Global Innovation Index (descriptive section) and the World Bank Enterprise Surveys (analytical section). The econometrics are a Crépon–Duguet–Mairesse (CDM) model in three steps: factors for propensity to invest in R&D, then to innovate, and, finally, innovation impacts on productivity. Results confirm the positive roles of factors, such as exports and education, in positive transmissions and uneven or insignificant results on productivity impacts from characteristics, such as age, size, and foreign ownership. The specifics for Kazakhstan suggest a potential for business innovation growth in the country. The paper concludes by suggesting key policy measures to unlock the potential for business innovation at a country level. Full article
(This article belongs to the Special Issue The Asian Economy: Constraints and Opportunities)
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<p>Dynamics of a two-step transmission from innovation inputs into outputs and impacts.</p>
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<p>Imbalance between inputs and outputs in Kazakhstan (source: elaborated based on the GII (2020)). <b>Note:</b> The linear regression line has an equation of Y = a + bX, where X is the explanatory variable and Y is the dependent variable. If the slope of the line is positive, then there is a positive linear relationship. This figure also plots confidence intervals.</p>
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<p>Innovation inputs of Central Asia and regional leaders (source: elaborated based on the GII (2020)). <b>Note:</b> The linear regression line has an equation of Y = a + bX, where X is the explanatory variable and Y is the dependent variable. If the slope of the line is positive, then there is a positive linear relationship.</p>
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<p>Innovation output of Central Asia and regional leaders (source: elaborated based on the GII (2020)). <b>Note:</b> The linear regression line has an equation of Y = a + bX, where X is the explanatory variable and Y is the dependent variable. If the slope of the line is positive, then there is a positive linear relationship.</p>
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17 pages, 13132 KiB  
Article
Effects of Herbaceous Plant Encroachment on the Soil Carbon Pool in the Shrub Tundra of the Changbai Mountains
by Xiaoyun Xu, Yinghua Jin, Jiawei Xu, Yingjie Zhang and Jiaxing Yang
Forests 2025, 16(2), 197; https://doi.org/10.3390/f16020197 - 22 Jan 2025
Viewed by 45
Abstract
Under global warming, vegetation composition changes induced by plant encroachment have a significant impact on the carbon balance of tundra ecosystems. The encroachment of herbaceous plants into indigenous shrub communities has changed the aboveground and belowground litter carbon input and the characteristics in [...] Read more.
Under global warming, vegetation composition changes induced by plant encroachment have a significant impact on the carbon balance of tundra ecosystems. The encroachment of herbaceous plants into indigenous shrub communities has changed the aboveground and belowground litter carbon input and the characteristics in the shrub tundra of the Changbai Mountains. However, the impact of variations in litter characteristics and litter carbon input on the dynamics of soil organic carbon (SOC) pool concentrations and SOC stability remains ambiguous. In this study, aboveground and belowground litter and soil samples were collected for lab experiments. Our results showed that the increase in aboveground litter and belowground litter due to Deyeuxia purpurea encroachment increased the SOC concentration. Simultaneously, D. purpurea encroachment decreased the soil C/N by decreasing the components of both aboveground and belowground litter that were resistant to decomposition (C/N and lignin/N) and increased the soil mineralization ability and available N concentrations, increased the CO2 release rate, and ultimately decreased the SOC concentration. D. purpurea encroachment enhanced soil decomposition capacity by increasing the concentration of organic carbon molecular structures, such as carbohydrates, in the aboveground and belowground litter, thereby increasing the concentration of decomposable organic carbon molecular structures and active organic carbon in the soil, while simultaneously reducing the concentration of recalcitrant organic carbon. Even more, D. purpurea encroachment reduced the recalcitrant components of the aboveground and belowground litter enhanced soil mineralization capability and increased soil nitrogen concentration, which collectively increased the carbon oxidation state (COX) and decreased SOC stability. In general, global warming has led to herbaceous plant encroachment, which changes the aboveground and belowground litter carbon inputs and properties in the tundra, in turn reducing the SOC concentration and soil carbon pool stability, enhancing soil carbon emission capacity, and increasing atmospheric CO2 concentration, forming a vicious cycle. Full article
(This article belongs to the Topic Plant Invasion)
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<p>Overview of the study area (<b>a</b>) and five types of tundra vegetation created by <span class="html-italic">Deyeuxia purpurea</span> encroachment (<b>b</b>).</p>
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<p>Histogram of the total carbon input, C/N and lignin/N of belowground and aboveground litter for various degrees of <span class="html-italic">Deyeuxia purpurea</span> encroachment. (<b>a</b>) Shows the total carbon input, (<b>b</b>) shows C/N, (<b>c</b>) shows lignin/N. Different lowercase letters indicate significant differences in the total carbon input, C/N, and lignin/N of aboveground litter (<span class="html-italic">p</span> &lt; 0.05), while distinct uppercase letters indicated differences in the total carbon input, C/N, and lignin/N of belowground litter (<span class="html-italic">p</span> &lt; 0.05). <span class="html-italic">Mil</span> (<span class="html-italic">D. purpurea</span> coverage was 30%), <span class="html-italic">Mod</span> (<span class="html-italic">D. purpurea</span> coverage was 50%), <span class="html-italic">Sev</span> (<span class="html-italic">D. purpurea</span> coverage was 70%), <span class="html-italic">Dey</span> (all <span class="html-italic">D. purpurea</span>), <span class="html-italic">Rho</span> (no <span class="html-italic">D. purpurea</span> encroachment, all <span class="html-italic">Rhododendron aureum</span>).</p>
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<p>Soil respiration rates with respect to the extent of <span class="html-italic">D. purpurea</span> encroachment in various months. Significant differences between sites at the same sampling time are indicated by distinct lowercase letters (<span class="html-italic">p</span> &lt; 0.05). The X-axis represents soil respiration rate from June to September, and “Average” represents the average soil respiration rate from June to September.</p>
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<p>Effects of different degrees of <span class="html-italic">Deyeuxia purpurea</span> encroachment on SOC concentration and COX. (<b>a</b>) SOC concentration, (<b>b</b>) COX. Significant differences between sites are indicated by different lowercase letters (<span class="html-italic">p</span> &lt; 0.05). <span class="html-italic">Mil</span> (<span class="html-italic">D. purpurea</span> coverage was 30%), <span class="html-italic">Mod</span> (<span class="html-italic">D. purpurea</span> coverage was 50%), <span class="html-italic">Sev</span> (<span class="html-italic">D. purpurea</span> coverage was 70%), <span class="html-italic">Dey</span> (all <span class="html-italic">D. purpurea</span>), <span class="html-italic">Rho</span> (no <span class="html-italic">D. purpurea</span> encroachment, all <span class="html-italic">Rhododendron aureum</span>).</p>
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<p>Changes in active organic carbons and molecular structure in the soil organic carbon according to the extent of <span class="html-italic">Deyeuxia purpurea</span> encroachment. Different letters denote significant differences between sites (<span class="html-italic">p</span> &lt; 0.05). (<b>a</b>) DOC concentration, (<b>b</b>) EOC concentration, (<b>c</b>) MBC concentration, (<b>d</b>) POC concentration, (<b>e</b>) MAOC concentration, (<b>f</b>) Molecular structure.</p>
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<p>Structural equation model (SEM) of the total aboveground and belowground litter carbon input (TLCI), aboveground and belowground litter properties (LP), soil properties (SP), and soil carbon emission (SCE) with SOC concentration (<b>a</b>). Standardized effects of driving factors on SOC concentration (<b>b</b>). SEM of aboveground and belowground litter components (LC), aboveground and belowground litter properties (LP), soil properties (SP), soil components (SC), and soil organic carbon pool (SOCP) with COX (<b>c</b>). Standardized effects of determinants of COX (<b>d</b>). Solid red lines and solid blue lines represent significantly positive and negative relationships, respectively. * 0.01 &lt; <span class="html-italic">p</span> &lt; 0.05; ** 0.001 &lt; <span class="html-italic">p</span> &lt; 0.01; *** <span class="html-italic">p</span> &lt; 0.001.</p>
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<p>Monthly variations in average temperature and precipitation in the Changbai Mountains tundra, 2022.</p>
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<p>Changes in molecular structure of organic carbon and COX in aboveground and belowground litters under different degrees of <span class="html-italic">Deyeuxia purpurea</span> encroachment. (<b>a</b>) Aboveground litter, (<b>b</b>) belowground litter, (<b>c</b>) COX.</p>
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<p>Correlation analysis of SOC and COX with various indicators in soil, aboveground litter, and belowground litter. (<b>a</b>) Soil, (<b>b</b>) aboveground litter, (<b>c</b>) belowground litter. * 0.01 &lt; <span class="html-italic">p</span> &lt; 0.05; ** 0.001 &lt; <span class="html-italic">p</span> &lt; 0.01; *** <span class="html-italic">p</span> &lt; 0.001.</p>
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<p>Variation in soil grain-size distribution.</p>
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16 pages, 7277 KiB  
Article
Geographic Information System and Multivariate Analysis Approach for Mapping Soil Contamination and Environmental Risk Assessment in Arid Regions
by Abdelbaset S. El-Sorogy, Khaled Al-Kahtany, Talal Alharbi, Rakan Al Hawas and Naji Rikan
Land 2025, 14(2), 221; https://doi.org/10.3390/land14020221 - 22 Jan 2025
Viewed by 95
Abstract
Heavy metal contamination in soil is a global issue threatening human health and ecosystems. Accurate spatial maps of heavy metals (HMs) are vital to mitigating the adverse effects on the ecosystem. This study utilizes GIS and multivariate analysis to evaluate HMs in agricultural [...] Read more.
Heavy metal contamination in soil is a global issue threatening human health and ecosystems. Accurate spatial maps of heavy metals (HMs) are vital to mitigating the adverse effects on the ecosystem. This study utilizes GIS and multivariate analysis to evaluate HMs in agricultural soils from Al Ghat Governorate, Saudi Arabia, analyzing Al, As, Co, Cr, Cu, Fe, Mn, Ni, Pb, V, and Zn using ICP-AES in 35 soil samples. Methods included contamination factor (CF), enrichment factor (EF), risk index (RI), geoaccumulation index (Igeo), pollution load index (PLI), soil quality guidelines (SQGs), and multivariate analysis. The soils, characterized by sandy texture, low organic matter, and alkalinity due to arid conditions and high calcium carbonate, had the following HM concentrations (mg/kg) in descending order: Fe (11,480) ˃ Al (7786) ˃ Mn (278) ˃ Zn (72.37) ˃ Ni (28.66) ˃ V (21.80) ˃ Cr (19.89) ˃ Co (19.00) ˃ Cu (12.46) ˃ Pb (5.46) ˃ As (2.69). EF, CF, and Igeo suggest natural sources for most HMs, predominantly from the sedimentary sequence, with localized Zn, Pb, Co, Mn, and Cu enrichment linked to mixed natural and agricultural influences. PLI and RI indicated acceptable contamination levels, posing no ecological risk. All samples fell below SQG thresholds for As, Cu, Pb, and Cr, confirming minimal ecological threat. Statistical analysis highlighted sedimentary cover as the primary HM source, with agricultural activities contributing to Co, Cu, Ni, and Pb levels. Full article
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<p>Location map of the sampling sites from Al Ghat farms, central Saudi Arabia.</p>
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<p>Comparison between LULC for the study area in 2013 and 2024.</p>
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<p>Spatial distribution of Al, As, Co, and Cr in Al Ghat agricultural soils.</p>
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<p>Q-mode HCA of soil samples.</p>
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<p>Spatial distribution of EF per sample locations for Pb, Zn, Ni, Cu, Mn, and Co in Al Ghat agricultural soils.</p>
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<p>R-mode HCA of the investigated HMs.</p>
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<p>The PCA scatter plot between the soil samples from the Al Ghat region and the HM variables.</p>
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31 pages, 6526 KiB  
Review
Remote Sensing Technology for Observing Tree Mortality and Its Influences on Carbon–Water Dynamics
by Mengying Ni, Qingquan Wu, Guiying Li and Dengqiu Li
Forests 2025, 16(2), 194; https://doi.org/10.3390/f16020194 - 21 Jan 2025
Viewed by 208
Abstract
Trees are indispensable to ecosystems, yet mortality rates have been increasing due to the abnormal changes in forest growth environments caused by frequent extreme weather events associated with global climate warming. Consequently, the need to monitor, assess, and predict tree mortality has become [...] Read more.
Trees are indispensable to ecosystems, yet mortality rates have been increasing due to the abnormal changes in forest growth environments caused by frequent extreme weather events associated with global climate warming. Consequently, the need to monitor, assess, and predict tree mortality has become increasingly urgent to better address climate change and protect forest ecosystems. Over the past few decades, remote sensing has been widely applied to vegetation mortality observation due to its significant advantages. Here, we reviewed and analyzed the major research advancements in the application of remote sensing for tree mortality monitoring, using the Web of Science Core Collection database, covering the period from 1998 to the first half of 2024. We comprehensively summarized the use of different platforms (satellite and UAV) for data acquisition, the application of various sensors (multispectral, hyperspectral, and radar) as image data sources, the primary indicators, the classification models used in monitoring tree mortality, and the influence of tree mortality. Our findings indicated that satellite-based optical remote sensing data were the primary data source for tree mortality monitoring, accounting for 80% of existing studies. Time-series optical remote sensing data have emerged as a crucial direction for enhancing the accuracy of vegetation mortality monitoring. In recent years, studies utilizing airborne LiDAR have shown an increasing trend, accounting for 48% of UAV-based research. NDVI was the most commonly used remote sensing indicator, and most studies incorporated meteorological and climatic factors as environmental variables. Machine learning was increasingly favored for remote sensing data analysis, with Random Forest being the most widely used classification model. People are more focused on the impacts of tree mortality on water and carbon. Finally, we discussed the challenges in monitoring and evaluating tree mortality through remote sensing and offered perspectives for future developments. Full article
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<p>(<b>a</b>) PRISMA 2020-based flowchart of the article selection process. (<b>b</b>) Searching string used in this study (TS = Topic; ALL = All Text).</p>
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<p>Trend of tree mortality remote sensing publications (1 January 1998–1 June 2024).</p>
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<p>The top twelve most productive (<b>a</b>) journals, (<b>b</b>) countries, (<b>c</b>) institutions, and (<b>d</b>) authors in publications of tree mortality remote sensing.</p>
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<p>The top twelve most productive (<b>a</b>) journals, (<b>b</b>) countries, (<b>c</b>) institutions, and (<b>d</b>) authors in publications of tree mortality remote sensing.</p>
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<p>The use frequency ratio of different remote sensing data sources in the studies of tree mortality.</p>
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<p>The proportions of different satellites used in tree mortality studies (“Other” includes Planet dove, Pléiades, Radarsat, ALOS, GeoEye, RapidEye, GRACE, and GF).</p>
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<p>Trends in the use of three types of optical satellite data in tree mortality research papers.</p>
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<p>Trends in the use of two types of radar in tree mortality studies.</p>
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<p>The proportions of the three airborne sensors used in the tree mortality study.</p>
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<p>Frequencies of three airborne sensors in tree mortality studies.</p>
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<p>Proportion of different combinations of remote sensing data used in tree mortality studies (“s” means satellite platform; “u” means drone platform).</p>
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<p>Different indicators utilized in the studies for tree mortality (NDVI = Normalized Difference Vegetation Index; ET = Evapotranspiration; LAI = Leaf Area Index; EVI =Enhanced Vegetation Index; NPP = Net Primary Productivity; GPP = Gross Primary Production; SR = Simple Ratio Index; NDWI = Normalized Difference Water Index; VOD = Vegetation Optical Depth; REP = Red Edge Position Index; MSI = Moisture Stress Index; NDMI = Normalized Difference Moisture Index; NDII = Normalized Difference Infrared Index; dNDVI = Differential Normalized Difference Vegetation Index; PSRI = Plant Senescence Reflectance Index; “Other” includes RGI = Red-Green Index, NDRE = Normalized Difference Red Edge Index, RVI = Ratio Vegetation Index, GNDVI = Green Normalized Difference Vegetation Index, MSAVI = Modified Soil Adjusted Vegetation Index, PRI = Photochemical Reflectance Index, CRI = Carotenoid Reflectance Index, and ARI = Anthocyanin Reflectance Index).</p>
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<p>Different ground-based variables utilized in the studies for tree mortality.</p>
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<p>Different classification methods utilized in the studies for tree mortality (RF = Random Forest, SVM = Support Vector Machine, DT = Decision Tree, GB = Gradient Boosting, LR = Linear Regression, NB = Naive Bayes, MLR = Multiple Linear Regression, ANN = Artificial Neural Network, SD = Self-developing, CNN = Convolutional Neural Network, DNN = Deep Neural Network, ML = Maximum Likelihood, ISODATA = Iterative self-organizing data analysis clustering algorithm, PCA = Principal Component Analysis, GLM = Generalized Linear Model, SOM = Self-organizing map, TSEB = Two Source Energy Balance) (the usage data of ANN model exclude CNN and DNN).</p>
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<p>Annual publications of different classification models in studies for tree mortality (“Other” includes Maximum Likelihood, Principal Component Analysis, Generalized Linear Model, Two Source Energy Balance, and Iterative self-organizing data analysis clustering algorithm).</p>
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<p>Studies use machine learning (<b>a</b>) and deep learning (<b>b</b>) to process different data sources for tree mortality.</p>
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<p>The proportions of the three influences studied in the reviewed papers.</p>
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<p>Trends in the research of the three influences in tree mortality papers.</p>
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12 pages, 1232 KiB  
Article
Biochar Application and Mowing Independently and Interactively Influence Soil Enzyme Activity and Carbon Sequestration in Karst and Red Soils in Southern China
by Wenjia Luo, Daniel F. Petticord, Shiwen Zhu, Shaowu Zhu, Yuanlong Wu, Xun Yi, Xinyue Wang, Yili Guo and Xuxin Song
Agronomy 2025, 15(1), 252; https://doi.org/10.3390/agronomy15010252 - 20 Jan 2025
Viewed by 321
Abstract
Soil organic carbon (SOC), a critical component of the global carbon cycle, represents the largest terrestrial carbon reservoir, and is thus a major component of influencing climate regulation and ecosystem health. Grasslands store substantial carbon in their soils, but this carbon reservoir is [...] Read more.
Soil organic carbon (SOC), a critical component of the global carbon cycle, represents the largest terrestrial carbon reservoir, and is thus a major component of influencing climate regulation and ecosystem health. Grasslands store substantial carbon in their soils, but this carbon reservoir is easily degraded by both grazing and mowing, particularly in vulnerable karst landscapes. This study investigates the potential of biochar, a carbon-rich soil amendment, as a management tool to maintain SOC or mitigate the degradation of SOC during mowing in karst grasslands in Southern China, using both red acidic and calcareous soils as experimental variables. T SOC fractions, soil enzyme activities, and soil pH were measured to determine the effect of mowing and biochar application on carbon stability and microbial activity. Consistent with expectations, mowing increases belowground biomass and promotes carbon loss through increased microbial activity, particularly in calcareous soils where mowing also decreases soil pH, increasing acidity and reducing the stability of Ca–carbon complexes. Biochar, however, counteracted these effects, increasing both particulate organic carbon (POC) and mineral-associated organic carbon (MAOC), especially in red soils where the addition of biochar greatly increased soil pH (from 5.4 to 6.33) (an effect not observed in the already-alkaline karst soils). Enzyme activities related to carbon degradation, such as β-D-Glucosidase and peroxidase, increased in biochar-amended soils (β-D-Glucosidase increased from 12.77 to 24.53 nmol/g/h and peroxidase increased from 1.1 to 2.36 mg/g/2h), each of which contribute to the degradation of carbon containing organic matter so that it may be ultimately stored in more recalcitrant forms. Mowing led to reduced polyphenol oxidase activity, but the presence of biochar mitigated these losses, protecting SOC pools (increased from 0.03 to 0.79 mg/g/2h). This study highlights biochar as an effective tool for enhancing SOC stability in karst grasslands, particularly in acidic soils, and suggests that integrating biochar into mowing regimes may optimize carbon sequestration while reducing fire risk. These findings offer valuable theoretical guidance for developing sustainable land management in sensitive ecosystems. Full article
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<p>Effect of mowing and biochar on soil particulate organic carbon (POC) (<b>a</b>) and mineral-associated organic carbon (MAOC) (<b>b</b>) in different soil types (no biochar, CK; with biochar, B; red soil, R; and calcareous soil, C). Values represent mean ± SE (<span class="html-italic">n</span> = 4). Different uppercase letters indicate significant differences among treatments under no mowing, different lowercase letters indicate significant differences among treatments under mowing (<span class="html-italic">p</span> ≤ 0.05). Asterisk indicates significant differences between mowing and no mowing treatments (* <span class="html-italic">p</span> &lt; 0.05; ** <span class="html-italic">p</span> &lt; 0.01; and *** <span class="html-italic">p</span> &lt; 0.001).</p>
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<p>Effect of mowing and biochar on polyphenol oxidase (PPO) (<b>a</b>), peroxidase (PER) (<b>b</b>), β-D-Glucosidase (βG) (<b>c</b>), and leucine aminopeptidase (LAP) (<b>d</b>) in different soil types (no biochar, CK; with biochar, B; red soil, R; and calcareous soil, C). Values represent mean ± SE (<span class="html-italic">n</span> = 4). Different uppercase letters indicate significant differences among treatments under no mowing, different lowercase letters indicate significant differences among treatments under mowing (<span class="html-italic">p</span> ≤ 0.05). Asterisk indicates significant differences between mowing and no mowing treatments (** <span class="html-italic">p</span> &lt; 0.01; and *** <span class="html-italic">p</span> &lt; 0.001).</p>
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<p>Effect of mowing and biochar on belowground biomass (<b>a</b>), pH (<b>b</b>), microbial biomass carbon (MBC) (<b>c</b>), ammonium nitrogen (NH<sub>4</sub>-N) (<b>d</b>), nitrate nitrogen (NO<sub>3</sub>-N) (<b>e</b>), and total available nitrogen (AN) (<b>f</b>) in different soil types (no biochar, CK; with biochar, B; red soil, R; and calcareous soil, C). Values represent mean ± SE (<span class="html-italic">n</span> = 4). Different uppercase letters indicate significant differences among treatments under no mowing, different lowercase letters indicate significant differences among treatments under mowing (<span class="html-italic">p</span> ≤ 0.05). Asterisk indicates significant differences between mowing and no mowing treatments (* <span class="html-italic">p</span> &lt; 0.05; ** <span class="html-italic">p</span> &lt; 0.01; and *** <span class="html-italic">p</span> &lt; 0.001).</p>
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18 pages, 4891 KiB  
Article
Monitoring Forest Disturbances and Associated Driving Forces in Guangdong Province Using Long-Term Landsat Time Series Images
by Lin Qiu, Zhongbing Chang, Xiaomei Luo, Songjia Chen, Jun Jiang and Li Lei
Forests 2025, 16(1), 189; https://doi.org/10.3390/f16010189 - 20 Jan 2025
Viewed by 387
Abstract
Research on monitoring forest disturbances and analyzing its driving factors is crucial for the sustainable management of forest ecosystems. To quantitatively identify the spatial distribution and dynamic changes of forest disturbance and its driving factors in Guangdong Province from 1990 to 2019, the [...] Read more.
Research on monitoring forest disturbances and analyzing its driving factors is crucial for the sustainable management of forest ecosystems. To quantitatively identify the spatial distribution and dynamic changes of forest disturbance and its driving factors in Guangdong Province from 1990 to 2019, the long-term Landsat time series imagery and the LandTrendr change detection algorithm were utilized. The impact of forest disturbances on four types of landscape fragmentation (attrition, perforation, shrinkage, and subdivision) was analyzed using the Forman index. The Geodetector model was used to analyze the driving factors of forest disturbance from human activity and the natural environment. The results showed that the LandTrendr algorithm achieved a Kappa coefficient of 0.79, with an overall accuracy of approximately 82.59%. The findings indicate a consistent increase in shrinkage patches, both in quantity and area. Spatially, the centroids of forest fragmentation processes exhibited a clear inland migration trend, reflecting the growing ecological pressures faced by inland forest ecosystems. Furthermore, interactions among driving factors, particularly between population density and economic factors, significantly amplified their combined impacts. The correlation between forest disturbances and socio-economic factors revealed distinct regional variations, highlighting significant differences in forest disturbance dynamics across cities with varying levels of economic development. This study provides critical insights into the spatiotemporal dynamics of forest disturbances under rapid urbanization and economic development. It lays the groundwork for sustainable forest management strategies in Guangdong Province and may contribute to global discussions on managing forest ecosystems during periods of rapid socio-economic transformation. Full article
(This article belongs to the Section Urban Forestry)
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<p>Location of the study area and spatial distribution of forests from GlobeLand30 (2020).</p>
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<p>Research technology roadmap.</p>
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<p>Construction process of forest subdivision process model (The red square is an example of an eight-neighborhood).</p>
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<p>Disturbance results for three typical areas ((<b>a</b>–<b>c</b>) were three representative areas).</p>
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<p>Result of centroid analysis in the spatial process of forest subdivision.</p>
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<p>Correlation coefficients between the area of forest disturbance and various factors.</p>
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20 pages, 7537 KiB  
Article
Diversity and Distribution of Phytophthora Species Along an Elevation Gradient in Natural and Semi-Natural Forest Ecosystems in Portugal
by Carlo Bregant, Eduardo Batista, Sandra Hilário, Benedetto Teodoro Linaldeddu and Artur Alves
Pathogens 2025, 14(1), 103; https://doi.org/10.3390/pathogens14010103 - 20 Jan 2025
Viewed by 340
Abstract
Globally, forests are constantly threatened by a plethora of disturbances of natural and anthropogenic origin, such as climate change, forest fires, urbanization, and pollution. Besides the most common stressors, during the last few years, Portuguese forests have been impacted by severe decline phenomena [...] Read more.
Globally, forests are constantly threatened by a plethora of disturbances of natural and anthropogenic origin, such as climate change, forest fires, urbanization, and pollution. Besides the most common stressors, during the last few years, Portuguese forests have been impacted by severe decline phenomena caused by invasive pathogens, many of which belong to the genus Phytophthora. The genus Phytophthora includes a large number of species that are invading forest ecosystems worldwide, chiefly as a consequence of global trade and human activities. This paper reports the results of a survey of Phytophthora diversity in natural and semi-natural forest ecosystems in Portugal along an elevation gradient. Isolations performed from 138 symptomatic plant tissues and rhizosphere samples collected from 26 plant species yielded a total of 19 Phytophthora species belonging to 6 phylogenetic clades, including P. cinnamomi (36 isolates), P. multivora (20), P. plurivora (9), P. cactorum (8), P. lacustris (8), P. pseudocryptogea (8), P. amnicola (6), P. hedraiandra (6), P. pseudosyringae (5), P. thermophila (5), P. bilorbang (4), P. inundata (4), P. asparagi (3), P. citricola (3), P. gonapodyides (3), P. rosacearum (3), P. chlamydospora (2), P. pachypleura (2), and P. syringae (1). Overall, the data obtained highlight the widespread occurrence of P. cinnamomi in natural ecosystems from sea level to mountain habitats. The results of the pathogenicity tests carried out on 2-year-old chestnut plants confirmed the key role of P. cinnamomi in the recrudescence of chestnut ink disease and the additional risk posed by P. pachypleura, P. plurivora, and P. multivora to Portuguese chestnut forests. Finally, three species, P. citricola, P. hedraiandra, and P. pachypleura, are reported for the first time in the natural ecosystems of Portugal. Full article
(This article belongs to the Special Issue Microbial Pathogenesis and Emerging Infections)
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<p>Overview of <span class="html-italic">Phytophthora</span> disease symptoms observed in coastal ecosystems (<b>a</b>–<b>e</b>), temperate (<b>f</b>–<b>j</b>), and montane forests (<b>k</b>–<b>o</b>) across Portugal: <span class="html-italic">Acacia longifolia</span> (<b>a</b>,<b>d</b>), <span class="html-italic">Pistacia lentiscus</span> (<b>b</b>), <span class="html-italic">Carpobrotus edulis</span> (<b>c</b>,<b>e</b>), <span class="html-italic">Quercus</span> spp. (<b>f</b>–<b>i</b>), <span class="html-italic">Rhododendron ponticum</span> (<b>j</b>), <span class="html-italic">Betula celtiberica</span> (<b>k</b>,<b>l</b>,<b>n</b>), <span class="html-italic">Castanea sativa</span> (<b>m</b>), and <span class="html-italic">Juniperus communis</span> (<b>o</b>). On the left, starting from the top, colony morphology of <span class="html-italic">Phytophthora amnicola</span>, <span class="html-italic">P. asparagi</span>, <span class="html-italic">P. bilorbang</span>, <span class="html-italic">P. cactorum</span>, <span class="html-italic">P. chlamydospora</span>, <span class="html-italic">P. cinnamomi</span>, <span class="html-italic">P. citricola</span>, <span class="html-italic">P. gonapodyides</span>, <span class="html-italic">P. hedraiandra</span>, <span class="html-italic">P. inundata</span>, <span class="html-italic">P. lacustris</span>, <span class="html-italic">P. multivora</span>, <span class="html-italic">P. pachypleura</span>, <span class="html-italic">P. plurivora</span>, <span class="html-italic">P. pseudocryptogea</span>, <span class="html-italic">P. pseudosyringae</span>, <span class="html-italic">P. rosacearum</span>, <span class="html-italic">P. syringae</span>, and <span class="html-italic">P. thermophila</span> after 7 days of growth at 20 °C on CA in the dark.</p>
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<p>Isolation frequency and distribution of the most common <span class="html-italic">Phytophthora</span> species isolated in this study.</p>
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<p>Distribution of <span class="html-italic">Phytophthora</span> species in Portugal. Red dots are occurrences for this study, black dots are from literature data, and blue dots in the background are for sampling areas.</p>
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<p><span class="html-italic">Phytophthora</span> diversity along the elevation gradient in Portugal. Data from the study and literature review.</p>
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<p>Maximum likelihood tree obtained from the internal transcribed spacer (ITS) sequences of <span class="html-italic">Phytophthora</span> species representative of the 12 clades. The tree was rooted to <span class="html-italic">Halophytophthora avicenniae</span> and <span class="html-italic">Nothophytophthora caduca</span>. Data are based on the General Time Reversible model. A discrete Gamma distribution was used to model evolutionary rate differences among sites. The tree is drawn to scale, with branch lengths measured in the number of substitutions per site. Bootstrap support values in percentage (1000 replicates) are given at the nodes. Ex-type cultures are in bold, and isolates obtained in this study are in red.</p>
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<p>Mean lesion length (±standard deviation) and symptoms on 2-year-old seedlings of <span class="html-italic">Castanea sativa</span> detected after 1 month from the inoculation with <span class="html-italic">Phytophthora</span> spp. Values with the same letter do not differ significantly at <span class="html-italic">p</span> = 0.05, according to the LSD multiple range test.</p>
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17 pages, 1335 KiB  
Article
The Sustainability Performance of Social Enterprises in China: The Configurational Impacts of Ecosystems and Revenue Structures
by Xiao-Min Yu, Hao-Yu Xia, Yi-Jun He and Hong-Yu Chen
Sustainability 2025, 17(2), 793; https://doi.org/10.3390/su17020793 - 20 Jan 2025
Viewed by 427
Abstract
Despite the global development of social enterprises (SEs) over the past three decades, how to improve sustainability remains a challenging issue for most SEs. Although SE ecosystems have been recognized as crucial determinants of SE sustainability performance in the current literature, no empirical [...] Read more.
Despite the global development of social enterprises (SEs) over the past three decades, how to improve sustainability remains a challenging issue for most SEs. Although SE ecosystems have been recognized as crucial determinants of SE sustainability performance in the current literature, no empirical study has comprehensively examined the relationships among them. Additionally, prior studies have demonstrated that sustainability performance might vary among SEs of different revenue structures or across different contexts, suggesting that more attention should be devoted to the complexity of the causal mechanisms determining SE sustainability performance. To address these gaps in the current literature, this paper examines the complex, divergent, and asymmetric causal links among SE ecosystems, revenue structures, and the sustainability performance of SEs in China by conducting fuzzy set qualitative comparative analysis (fsQCA) of 274 typical cases of SEs. The results revealed alternative configurations for high and low levels of sustainability performance among SEs of different revenue structures. First, the fsQCA results indicated that SE sustainability performance was not determined by the impacts of single components of SE ecosystems but rather by the combined effects of multiple elements. Second, for SEs of divergent revenue structures, causal paths leading to high or low levels of sustainability performance showed notable discrepancies in terms of both number and composition. Specifically, commercial SEs receiving income mainly from market-based earned income were more likely to achieve higher levels of social and financial sustainability because of greater adaptability to SE ecosystems and less environmental dependence. Third, the impacts of different components of SE ecosystems on sustainable performance also varied with SE revenue structures. Three categories of components—policy environment, sociocultural setting, and industrial infrastructure—made more important contributions to SE sustainability performance in both the social and financial dimensions. Full article
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<p>Configurational framework.</p>
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19 pages, 526 KiB  
Article
Nutritional Vulnerability of Displaced Persons: A Study of Food Security and Access in Kumba Municipality, Cameroon
by Kevin N. Metuge, Betrand A. Tambe, Fabrice Tonfack Djikeng, Aduni Ufuan Achidi, Given Chipili and Xikombiso G. Mbhenyane
Challenges 2025, 16(1), 7; https://doi.org/10.3390/challe16010007 - 20 Jan 2025
Viewed by 362
Abstract
Concerns about global food insecurity have been growing, particularly in low- and middle-income countries. This study aimed to assess the determinants of food security among internally displaced persons (IDPs)—people who have been forced to flee their homes due to conflict, natural disasters, or [...] Read more.
Concerns about global food insecurity have been growing, particularly in low- and middle-income countries. This study aimed to assess the determinants of food security among internally displaced persons (IDPs)—people who have been forced to flee their homes due to conflict, natural disasters, or other crises—and their children under five, as well as the influence on their nutritional status. Using random sampling, the caregivers of IDPs and children under five in households were included in the study. The caregivers were interviewed using a validated structured questionnaire, while nutritional assessments of both children and adults were conducted through anthropometric and clinical evaluation methods. The findings revealed a high prevalence of food insecurity, with 97.6% of IDP households experiencing some degree of insecurity. Additionally, 28.3% of the surveyed households had high dietary diversity. Among the children, 50.6% were stunted, over a third were underweight, and 15.8% were wasted, indicating severe nutritional deficiencies. Among adults, 28.4% were overweight or obese, while a significant number were underweight. Multiple linear regression analysis showed that the caregivers’ monthly salary and the average amount spent on food were associated with a decrease in food insecurity. Conversely, large household sizes and coping strategies employed to mitigate food insecurity were linked to increased food insecurity. In conclusion, the study highlights a high prevalence of food insecurity among IDP households, forcing families to adopt coping strategies, mainly through dietary modifications. This, in turn, contributes to low dietary diversity and poor nutritional status, with children suffering from underweight, wasting, and stunting. These findings underscore the urgent need for comprehensive interventions, including the distribution of food vouchers, cash transfers, food banks, and support for home gardening and small-scale farming, as well as education on meal rationing, meal planning, and family planning services. Addressing the root causes of food insecurity—namely low household income and large family sizes—can improve access to nutritious food and ensure the health and well-being of IDPs. Furthermore, addressing food insecurity within this vulnerable group is critical to the broader goals of planetary health, as it highlights the intersection of human health, social equity, and environmental sustainability. By promoting sustainable food systems and supporting vulnerable populations, these interventions can contribute to the resilience of both communities and eco-systems in the face of ongoing global challenges. Full article
(This article belongs to the Section Food Solutions for Health and Sustainability)
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<p>Household food security of surveyed IDP households in the Kumba Municipality (<span class="html-italic">n</span> = 270).</p>
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16 pages, 2626 KiB  
Article
Human Activity as a Growing Threat to Marine Ecosystems: Plastic and Temperature Effects on the Sponge Sarcotragus spinosulus
by Jessica Lombardo, Maria del Mar Ribas-Taberner, Maria Magdalena Quetglas-Llabrés, Samuel Pinya, Llorenç Gil, Silvia Tejada, Antoni Sureda and Montserrat Compa
Toxics 2025, 13(1), 66; https://doi.org/10.3390/toxics13010066 - 20 Jan 2025
Viewed by 612
Abstract
Human activities increasingly threaten marine ecosystems through rising waste and temperatures. This study investigated the role of plastics as vectors for Vibrio bacteria and the effects of temperature on the marine sponge Sarcotragus spinosulus. Samples of plastics and sponges were collected during [...] Read more.
Human activities increasingly threaten marine ecosystems through rising waste and temperatures. This study investigated the role of plastics as vectors for Vibrio bacteria and the effects of temperature on the marine sponge Sarcotragus spinosulus. Samples of plastics and sponges were collected during July, August (high-temperature period), and November (lower-temperature period). Bacterial growth and sponge responses were analysed using biochemical biomarkers. The results revealed a peak in colony-forming units (CFU), particularly of Vibrio alginolyticus, on plastics and sponges in August, followed by a decrease in November. In August, CFU counts of Vibrio spp. were significantly higher in sponges with poor external appearance (characterized by dull coloration and heavy epiphytic growth) but returned to levels observed in healthy sponges by November. Microplastics were detected in the tissues of both sponge groups, with higher concentrations found in affected specimens. Biomarker analyses revealed increased lysozyme, glutathione S-transferase, catalase, and superoxide dismutase activities in healthy sponges during August, while malondialdehyde levels, indicating oxidative damage, were higher in affected sponges. In conclusion, affected sponges exhibited elevated CFU counts of Vibrio spp. and reduced antioxidant and detoxification responses under elevated temperatures. These findings suggest that combined impacts of plastics and warming may pose significant risks to S. spinosulus in the context of global climate change. Full article
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<p>Representative images of (<b>A</b>) healthy and (<b>B</b>) affected specimens of <span class="html-italic">Sarcotragus spinosulus</span>.</p>
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<p>Geographic location of the study area for Portals Vells in the Balearic Islands, western Mediterranean Sea: (<b>A</b>) Balearic archipelago showing Mallorca, Menorca, Ibiza, and Formentera islands; (<b>B</b>) detailed view of study area on the southwest coast on the island of Mallorca (red rectangle); (<b>C</b>) aerial photograph of the study site showing the sampling area (red rectangle).</p>
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<p>Daily temperature variation (24–25 August), showing values exceeding 29 °C for more than 5 h.</p>
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<p>Number of <span class="html-italic">Vibrio</span> spp. colonies (CFU) in the plastics across the three sampling months. Note: * indicates significant differences respect July and November, and # respect to November, <span class="html-italic">p</span> &lt; 0.05. n.d.—none detected.</p>
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<p>Number of <span class="html-italic">Vibrio</span> spp. colonies (CFU) in <span class="html-italic">Sarcotragus spinosulus</span> samples collected during the three sampling months, differentiated by healthy and affected specimens. Note: * indicates significant differences respect July and November; # respect to November within the same experimental group: affected or healthy; <span>$</span> indicates significant differences between affected and healthy sponges, <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Example of images of microplastic particles found in <span class="html-italic">Sarcotragus spinosulus</span> at Portals Vells: (<b>A</b>) blue irregular fragment; (<b>B</b>) blue fibre; (<b>C</b>) red fibre; (<b>D</b>) blue irregular fragment.</p>
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<p>Biomarkers of oxidative stress—(<b>A</b>) catalase and (<b>B</b>) superoxide dismutase (SOD) activities, (<b>C</b>) glutathione levels (GSH), and (<b>D</b>) malondialdehyde levels (MDA)—in <span class="html-italic">Sarcotragus spinosulus</span> in the three sampling periods. * Significant differences between the involved groups at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Activity of lysozyme in <span class="html-italic">Sarcotragus spinosulus</span> in the three sampling periods. * Significant differences between the involved groups at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Activity of glutathione s-transferase (GST) in <span class="html-italic">Sarcotragus spinosulus</span> in the three sampling periods. * Significant differences between the involved groups at <span class="html-italic">p</span> &lt; 0.05.</p>
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16 pages, 878 KiB  
Entry
From ONE Health to ONE Paleopathology: Deep-Time Perspectives on Health in the Face of Climate and Environmental Change
by Gwen Robbins Schug and Jane E. Buikstra
Encyclopedia 2025, 5(1), 13; https://doi.org/10.3390/encyclopedia5010013 - 20 Jan 2025
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Definition
This entry explores the emergence of ONE Paleopathology as a holistic, interdisciplinary approach to understanding health through deep time. The entry discusses key areas where paleopathological research provides crucial insights: animals as sentinels of environmental health, the evolution and transmission of infectious diseases, [...] Read more.
This entry explores the emergence of ONE Paleopathology as a holistic, interdisciplinary approach to understanding health through deep time. The entry discusses key areas where paleopathological research provides crucial insights: animals as sentinels of environmental health, the evolution and transmission of infectious diseases, the impacts of urbanization and pollution on human health, and the effects of climate change on disease patterns. Special attention is given to case studies involving malaria, tuberculosis, and environmental toxicity, demonstrating how past human–environment interactions inform current health strategies. The entry also emphasizes the importance of indigenous and local knowledge (ILK) systems in understanding and managing health challenges, highlighting how traditional ecological knowledge complements scientific approaches. By bridging past and present, ONE Paleopathology offers valuable perspectives for addressing modern health challenges in the context of accelerating environmental change, while promoting more equitable and sustainable approaches to global health. Full article
(This article belongs to the Collection Encyclopedia of One Health)
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<p>ONE Paleopathology approaches to environmental health in the past. Created in BioRender (Robbins Schug, G. <a href="https://BioRender.com/k77k949" target="_blank">https://BioRender.com/k77k949</a>, accessed on 1 January 2025).</p>
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31 pages, 9739 KiB  
Article
Spatiotemporal Relationship Between Carbon Metabolism and Ecosystem Service Value in the Rural Production–Living–Ecological Space of Northeast China’s Black Soil Region: A Case Study of Bin County
by Yajie Shang, Yuanyuan Chen, Yalin Zhai and Lei Wang
Land 2025, 14(1), 199; https://doi.org/10.3390/land14010199 - 19 Jan 2025
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Abstract
Amid global climate challenges and an urgent need for ecological protection, the northeastern black soil region—one of the world’s remaining “three major black soil regions”—confronts significant tensions between agricultural economic development and land ecological protection, threatening national food security. Based on the “production–ecology–life” [...] Read more.
Amid global climate challenges and an urgent need for ecological protection, the northeastern black soil region—one of the world’s remaining “three major black soil regions”—confronts significant tensions between agricultural economic development and land ecological protection, threatening national food security. Based on the “production–ecology–life” (PLE) classification system, this study established a dual-dimensional evaluation for carbon metabolism and ESV in horizontal and vertical dimensions. The horizontal flow of carbon and ESV was traced across different ecosystems, while the spatial and temporal dynamics of carbon metabolism and ESV were analyzed vertically. Spatial autocorrelation analyses were employed to examine the interaction patterns between carbon metabolism and ESV. The findings reveal that (1) cropland production space remains the dominant spatial type, exhibiting fluctuating patterns in the size of other spatial types, with a notable reduction in water ecological space. (2) From 2000 to 2020, high-value carbon metabolism density areas were primarily concentrated in the central region, while low-value areas gradually decreased in size. Cropland production space and urban living space served as key compartments and dominant pathways for carbon flow transfer in the two periods, respectively. (3) The total ecosystem service value (ESV) showed a downward trend, decreasing by CNY 1.432 billion from 2000 to 2020. The spatial distribution pattern indicates high values in the center and northwest, contrasting with lower values in the southeast. The flow of ecological value from forest ecological space to cropland production space represents the main loss pathway. (4) A significant negative correlation exists between carbon metabolism density and ESV, with areas of high correlation predominantly centered around cropland production space. This study provides a scientific foundation for addressing the challenges facing the black soil region, achieving synergistic resource use in pursuit of carbon neutrality, and constructing a more low-carbon and sustainable spatial pattern. Full article
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<p>Spatial carbon metabolism and ESV horizontal and vertical transfer processes.</p>
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<p>(<b>a</b>) Location map of Heilongjiang province. (<b>b</b>) Location map of Harbin city. (<b>c</b>) Location map of Bin county. (<b>d</b>) Map of the research area.</p>
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<p>Research methodology flow chart.</p>
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<p>Spatial and temporal distribution of PLE in Bin County from 2000 to 2020.</p>
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<p>Heat map of land use transfer in Bin County from 2000 to 2020.</p>
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<p>Sankey diagram of land use transfer in PLE space in Bin County from 2000 to 2020.</p>
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<p>Spatial distribution map of carbon metabolism density in Bin County from 2000 to 2020.</p>
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<p>Heat map of carbon flow in Bin County from 2000 to 2020.</p>
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<p>Sankey diagram of carbon flows in PLE space in Bin County from 2000 to 2020.</p>
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<p>Spatial distribution map of ecosystem service value intensity in Bin County from 2000 to 2020.</p>
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<p>Heat map of ESV gains and losses in Bin County from 2000 to 2020.</p>
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<p>Sankey diagram of ecological value gains and losses in PLE space in Bin County.</p>
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<p>Bivariate Moran’s index for the production–living–ecological space from 2000 to 2020.</p>
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<p>LISA cluster graph of carbon metabolism and ESV in the PLE during 2000–2020.</p>
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<p>Development of zoning management measures in the study area based on distinct clustering patterns.</p>
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22 pages, 3050 KiB  
Review
The Role of Pathogens in Bumblebee Decline: A Review
by Huanhuan Chen, Nawaz Haider Bashir, Qiang Li, Chao Liu, Muhammad Naeem, Haohan Wang, Wenrong Gao, Richard T. Corlett, Cong Liu and Mayra C. Vidal
Pathogens 2025, 14(1), 94; https://doi.org/10.3390/pathogens14010094 - 18 Jan 2025
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Abstract
Bumblebees, the most important wild pollinators in both agricultural and natural ecosystems, are declining worldwide. The global decline of bumblebees may threaten biodiversity, pollination services, and, ultimately, agricultural productivity. Several factors, including pesticide usage, climate change, habitat loss, and species invasion, have been [...] Read more.
Bumblebees, the most important wild pollinators in both agricultural and natural ecosystems, are declining worldwide. The global decline of bumblebees may threaten biodiversity, pollination services, and, ultimately, agricultural productivity. Several factors, including pesticide usage, climate change, habitat loss, and species invasion, have been documented in the decline of bumblebee species, but recent studies have revealed the dominating role of pathogens and parasites over any of these causes. Unfortunately, there is a lack of a full understanding of the role of pathogens and parasites in the decline of bumblebee species. The current study provides a comprehensive review of how pathogens and parasites contribute to the decline of bumblebee species. The study also explores the prevalence of each pathogen and parasite within bumblebee populations. Furthermore, we address the synergistic effects of pathogens and other stressors, such as pesticides, climatic effects, and habitat loss, on bumblebee populations. To summarize, we propose possible conservation and management strategies to preserve the critical role of bumblebees in pollination services and thus to support ecosystem and agricultural health. Full article
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<p>Factors affecting bumblebees’ health (references in the text).</p>
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<p>Flowchart of the literature search and screening process in this study.</p>
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<p>Distribution and prevalence of bumblebee pathogens (points represent the country-level prevalence of pathogens, not the exact locations of pathogens).</p>
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<p><span class="html-italic">Bombus terrestris</span>: (<b>A</b>) healthy colony, (<b>B</b>) healthy fourth instar larva, (<b>C</b>) healthy adult, (<b>D</b>–<b>F</b>) <span class="html-italic">Ascosphaera apis</span> chalkbrood-infected fourth instar larvae, (<b>G</b>–<b>I</b>) deformed wing virus infected adults; scale bars = 50 mm (<b>B</b>,<b>D</b>–<b>F</b>), 5 mm (<b>C</b>,<b>G</b>–<b>H</b>) (sources: Zhang et al. [<a href="#B78-pathogens-14-00094" class="html-bibr">78</a>] (<b>A</b>), Pereira et al. [<a href="#B16-pathogens-14-00094" class="html-bibr">16</a>] (<b>B</b>,<b>D</b>–<b>F</b>), and Cilia et al. [<a href="#B15-pathogens-14-00094" class="html-bibr">15</a>] (<b>C</b>,<b>G</b>–<b>I</b>)).</p>
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<p>Interaction between environmental changes and pathogen dynamics, and their impacts on bumblebees.</p>
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