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Forests, Volume 15, Issue 11 (November 2024) – 186 articles

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28 pages, 31172 KiB  
Article
Optimizing GEDI Canopy Height Estimation and Analyzing Error Impact Factors Under Highly Complex Terrain and High-Density Vegetation Conditions
by Runbo Chen, Xinchuang Wang, Xuejie Liu and Shunzhong Wang
Forests 2024, 15(11), 2024; https://doi.org/10.3390/f15112024 (registering DOI) - 17 Nov 2024
Abstract
The Global Ecosystem Dynamics Investigation (GEDI) system provides essential data for estimating forest canopy height on a global scale. However, factors such as complex topography and dense canopy can significantly reduce the accuracy of GEDI canopy height estimations. We selected the South Taihang [...] Read more.
The Global Ecosystem Dynamics Investigation (GEDI) system provides essential data for estimating forest canopy height on a global scale. However, factors such as complex topography and dense canopy can significantly reduce the accuracy of GEDI canopy height estimations. We selected the South Taihang region of Henan Province, China, as our study area and proposed an optimization framework to improve GEDI canopy height estimation accuracy. This framework includes correcting geolocation errors in GEDI footprints, screening and analyzing features that affect estimation errors, and combining two regression models with feature selection methods. Our findings reveal a geolocation error of 4 to 6 m in GEDI footprints at the orbital scale, along with an overestimation of GEDI canopy height in the South Taihang region. Relative height (RH), waveform characteristics, topographic features, and canopy cover significantly influenced the estimation error. Some studies have suggested that GEDI canopy height estimates for areas with high canopy cover lead to underestimation, However, our study found that accuracy increased with higher canopy cover in complex terrain and dense vegetation. The model’s performance improved significantly after incorporating the canopy cover parameter into the optimization model. Overall, the R² of the best-optimized model was improved from 0.06 to 0.61, the RMSE was decreased from 8.73 m to 2.23 m, and the rRMSE decreased from 65% to 17%, resulting in an accuracy improvement of 74.45%. In general, this study reveals the factors affecting the accuracy of GEDI canopy height estimation in areas with complex terrain and dense vegetation cover, on the premise of minimizing GEDI geolocation errors. Employing the proposed optimization framework significantly enhanced the accuracy of GEDI canopy height estimates. This study also highlighted the crucial role of canopy cover in improving the precision of GEDI canopy height estimation, providing an effective approach for forest monitoring in such regions and vegetation conditions. Future studies should further improve the classification of tree species and expand the diversity of sample tree species to test the accuracy of canopy height estimated by GEDI in different forest structures, consider the distortion of optical remote sensing images caused by rugged terrain, and further mine the information in GEDI waveforms so as to enhance the applicability of the optimization framework in more diverse forest environments. Full article
(This article belongs to the Section Forest Inventory, Modeling and Remote Sensing)
22 pages, 6256 KiB  
Article
Developing a Method to Estimate Above-Ground Carbon Stock of Forest Tree Species Pinus densata Using Remote Sensing and Climatic Data
by Kai Luo, Yafei Feng, Yi Liao, Jialong Zhang, Bo Qiu, Kun Yang, Chenkai Teng and Tangyan Yin
Forests 2024, 15(11), 2023; https://doi.org/10.3390/f15112023 (registering DOI) - 16 Nov 2024
Viewed by 335
Abstract
Forest above-ground carbon stock (AGCS) is one of the primary ecological evaluation indicators, so it is crucial to estimate the AGCS accurately. In this research, we added the climatic and topographic factors to the estimation process by a remote sensing approach to explore [...] Read more.
Forest above-ground carbon stock (AGCS) is one of the primary ecological evaluation indicators, so it is crucial to estimate the AGCS accurately. In this research, we added the climatic and topographic factors to the estimation process by a remote sensing approach to explore their impact and to achieve more precise estimations. We hope to develop a more accurate estimation method for AGCS based on remote sensing data and climate data. The random forest (RF) method has good robustness and wide applicability. Therefore, we modeled and predicted the AGCS by RF based on sixty field sample plots of Pinus densata pure forests in southwest China and the factors extracted from Landsat 8 OLI images (source I), Sentinel-2A images (source II), and combined Landsat 8 OLI and Sentinel-2A images (source III). We added the topographic and climatic factors to establish the AGCS estimation model and compared the results. The topographic factors contain elevation, slope, and aspect. Climatic factors contain mean annual temperature, annual precipitation, annual potential evapotranspiration, and monthly mean potential evapotranspiration. It was found that the R2 and RMSE of the model based on source III were better than the R2 and RMSE of the models based on source I and source II. Compared to the models based on source I and source II, the model based on source III improved R2 by up to 0.08, reduced RMSE by up to 2.88 t/ha, and improved P by up to 4.29%. Among the models without adding factors, the model based on source III worked the best, with an R2 of 0.87, an RMSE of 10.81 t/ha, an rRMSE of 23.19%, and a P of 79.71%. Among the models that added topographic factors, the model based on source III worked best after adding elevation, with an R2 of 0.89, an RMSE of 10.01 t/ha, an rRMSE of 21.47%, and a P of 82.17%. Among the models that added climatic factors, the model that added the annual precipitation factor had the best modeling result, with an R2 of 0.90, an RMSE of 9.53 t/ha, an rRMSE of 20.59%, and a P of 83.00%. The prediction result exhibited that the AGCS of the Pinus densata forest in 2021 was 9,737,487.52 t. The combination of Landsat 8 OLI and Sentinel-2A could improve the prediction accuracy of the AGCS. The addition of annual precipitation can effectively improve the accuracy of AGCS estimation. Higher resolution of climate data is needed to enhance the modeling in future work. Full article
18 pages, 9757 KiB  
Article
Global Warming Will Drive Spatial Expansion of Prunus mira Koehne in Alpine Areas, Southeast Qinghai–Tibet Plateau
by Jinkai Gu, Qiang He, Qingwan Li, Qinglin Li, Shengjian Xiang, Wanchi Li, Aohang Jin, Shunbin Wang, Feipeng Liu and Guoyong Tang
Forests 2024, 15(11), 2022; https://doi.org/10.3390/f15112022 (registering DOI) - 16 Nov 2024
Viewed by 337
Abstract
Abstract: Global climate change exerts great effects on plant distributions. However, the response of Prunus mira Koehne, one of the most important species for ecological protection in the southeast of the Qinghai–Tibet Plateau, to climate change remains unclear. To explore the ecological factors [...] Read more.
Abstract: Global climate change exerts great effects on plant distributions. However, the response of Prunus mira Koehne, one of the most important species for ecological protection in the southeast of the Qinghai–Tibet Plateau, to climate change remains unclear. To explore the ecological factors affecting the distribution of P. mira in the context of global climate change, the MaxENT model is used to predict suitable habitats for P. mira. Our study indicated that the distribution of Prunus mira Koehn is primarily influenced by temperature rather than precipitation, and warming can facilitate the growth of P. mira. When the temperature seasonality (bio4) ranges from 134 to 576 and the mean temperature of the coldest quarter (bio11) ranges from −2.6 °C to 2.7 °C, it is most conducive to the growth of P. mira. Among the four climate scenarios, the optimal habitat for P. mira is predominantly concentrated in river valley areas and is expected to expand into higher altitude regions, particularly in the north and southeast. SSP245 and SSP370 climate pathways are conducive to the growth and spatial expansion of P. mira. Our findings highlight the significant impact of temperature not precipitation on the distribution of P. mira, and this insight is crucial for the stability and conservation of this ecologically significant plant species. Full article
(This article belongs to the Section Forest Ecology and Management)
13 pages, 1029 KiB  
Article
A Combination of Traditional and Mechanized Logging for Protected Areas
by Natascia Magagnotti, Benno Eberhard and Raffaele Spinelli
Forests 2024, 15(11), 2021; https://doi.org/10.3390/f15112021 (registering DOI) - 16 Nov 2024
Viewed by 192
Abstract
Teaming draught animals with modern forest machines may offer an innovative low-impact solution to biomass harvesting in protected areas. Machine traffic only occurs on pre-designated access corridors set 50 m apart, while trees are cut with chainsaws and dragged to the corridor’s edge [...] Read more.
Teaming draught animals with modern forest machines may offer an innovative low-impact solution to biomass harvesting in protected areas. Machine traffic only occurs on pre-designated access corridors set 50 m apart, while trees are cut with chainsaws and dragged to the corridor’s edge by draught horses. The operation presented in this study included one chainsaw operator, two draught horses with their driver, an excavator-based processor with its driver and a helper equipped with a chainsaw for knocking off forks and large branches, and a light forwarder (7 t) with his driver. Researchers assessed work productivity and harvesting cost through a time study repeated on 20 sample plots. Descriptive statistics were used to estimate productivity and cost benchmark figures, which were matched against the existing references for the traditional alternatives. The new system achieved a productivity in excess of 4 m3 over bark per scheduled hour (including delays). Harvesting cost averaged EUR 53 m−3, which was between 15% and 30% cheaper than the traditional alternatives. What is more, the new system increased labor and horse productivity by a factor of 2 and 7, respectively, which can effectively counteract the increasingly severe shortage of men and animals. Full article
28 pages, 36390 KiB  
Article
Scenic Influences on Walking Preferences in Urban Forest Parks from Top-View and Eye-Level Perspectives
by Jiahui Zou, Hongchao Jiang, Wenjia Ying and Bing Qiu
Forests 2024, 15(11), 2020; https://doi.org/10.3390/f15112020 (registering DOI) - 16 Nov 2024
Viewed by 222
Abstract
Urban forest parks offer valuable spaces for walking activities that benefit both physical and mental health. However, trails in current park designs are often underutilised, and the scene layout does not fully meet the preferences of walkers. Therefore, understanding the connection between scene [...] Read more.
Urban forest parks offer valuable spaces for walking activities that benefit both physical and mental health. However, trails in current park designs are often underutilised, and the scene layout does not fully meet the preferences of walkers. Therefore, understanding the connection between scene characteristics and walking preferences is essential. This study aimed to develop an ensemble protocol to assess the role of scene characteristics in walking preferences, using Shanghai Gongqing Forest Park as an illustrative example. A walking preference heat map was created using a combination of crowdsourced GPS data. The scene characteristics were quantified using panoramic photographs, drone orthophotos, computer vision, and deep learning techniques. Taking spatial dependence into account, the key findings include the following: (1) From an overhead view, the shortest paths, waterbody density, and recreational facility selection positively influenced walking preferences, while secondary asphalt trails had a negative effect. (2) At the eye level, aesthetically pleasing landscape elements, such as flowers and bridges, attracted more pedestrians, while closed trails were less favoured. (3) Eye-level features explained 43.5% of the variation in walking preference, with a stronger influence on walking preference compared to 22.4% for overhead features. (4) Natural elements were generally more significant than artificial ones; the feature ranking of significant impact was flowers > NACHr1000 > visual perception > water body density > bridge > SVF > retail > entertainment > asphalt. This study proposes a flexible protocol that provides urban forest park managers and planners with practical tools to create a more walker-friendly environment and more accurate trail alignment, as well as a solid empirical basis for assessing the use of urban forest parks. Full article
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Figure 1
<p>The extent of Gongqing Forest Park, Shanghai, China: (<b>a</b>) the orthographic projection; (<b>b</b>) the site location in Shanghai.</p>
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<p>The protocol of assessing the influence of scene characteristics on walking preference in urban forest parks.</p>
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<p>GPS locations from crowdsourced data. GPS locations of all walkers in the Gongqing Forest Park from the (<b>a</b>) 2Bulu and (<b>b</b>) Foooooot applications. Gross data from 2017 to 2024 were collected.</p>
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<p>Illustration of the process of on-site observation with the panorama camera and the positioning of photos: (<b>a</b>) the illustration of a panoramic camera by on-site observation; (<b>b</b>) the form of dichotomous scene-characteristic variables that need to be recorded manually; (<b>c</b>) an illustration of the position of panoramic photos.</p>
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<p>Semantic segmentation based on PSPNet. (<b>a</b>,<b>c</b>,<b>d</b>) The area within the red dashed line is where we extract the eye-level scene characteristics; (<b>a</b>,<b>b</b>) the area within the black dashed line is where we calculate the SVF value; (<b>e</b>) the semantic segmentation result; (<b>f</b>) the fisheye conversion process and the result of calculating the SVF.</p>
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<p>Schematic overview of subjective perception variables: (<b>a</b>) one sample of scoring for objective perception (scene encoding: 003); (<b>b</b>) a few examples of high and low scores.</p>
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<p>KDE heat map and the value of walking preference for each on-site observation point: (<b>a</b>) KDE plot for walking preference; (<b>b</b>) the raster value extracted from the KDE plot of each on-site observation point; (<b>c</b>,<b>d</b>) the walking preference data distribution trends of the KDE and points, respectively.</p>
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<p>Significant variables of scene characteristics correlated with walking preference and the ranking importance of the significant variables.</p>
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<p>Pearson correlations among the 24 significant variables, where grey parts are the retained variables that can be used for the OLS analysis. Notes: * <span class="html-italic">p</span> &lt; 0.1; ** <span class="html-italic">p</span> &lt; 0.05; *** <span class="html-italic">p</span> &lt; 0.001.</p>
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<p>The left figure shows the residual Moran’s I for OLS; the right shows the residual Moran’s I for SAC.</p>
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<p>Model performance of random forest, and the ranking importance of significant variables: (<b>a</b>) the fitting of the training and test sets in the random forest and the status of the performance evaluation metrics; (<b>b</b>) the summary plot of SHAP, showing the ranking of gross variables.</p>
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<p>The SHAP dependence of each key factor is displayed in box plots.</p>
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19 pages, 1705 KiB  
Article
Predicting Operational Events in Mechanized Weed Control Operations by Offline Multi-Modal Data and Machine Learning Provides Highly Accurate Classification in Time Domain
by Stelian Alexandru Borz and Andrea Rosario Proto
Forests 2024, 15(11), 2019; https://doi.org/10.3390/f15112019 (registering DOI) - 15 Nov 2024
Viewed by 242
Abstract
Monitoring of operations has become a critical activity in forestry, aiming to provide the data required by planning and production management. Conventional methods, on the other hand, come at a high expense of resources. A neural network was trained, validated, and tested in [...] Read more.
Monitoring of operations has become a critical activity in forestry, aiming to provide the data required by planning and production management. Conventional methods, on the other hand, come at a high expense of resources. A neural network was trained, validated, and tested in this study based on multi-modal data to classify relevant operational events in mechanized weed control operations. The architecture of a neural network was tuned in terms of the number of hidden layers and neurons, and the regularization term was set at various values to obtain optimally tuned models for three data modalities: triaxial acceleration data coupled with speed extracted from GNSS signals (AS), triaxial acceleration (A), and speed alone (S). In the training and validation phase, the models based on AS and A achieved a very high classification accuracy, accounting for 92 to 93% when considering four relevant events. In the testing phase, which was run on unseen data, the classification accuracy reached figures of 91 to 92%, indicating a good generalization ability of the models. The results point out that multimodal data are able to provide the features for distinguishing events and add spatial context to the monitored operations, standing as a suitable solution for offline, partly automated monitoring. Future studies are required to see how the capabilities of online, real-time technologies such as deep learning coupled with computer vision can add more context and improve classification performance. Full article
(This article belongs to the Special Issue Sustainable Forest Operations Planning and Management)
18 pages, 4511 KiB  
Article
Spatial Variability of Soil CO2 Emissions and Microbial Communities in a Mediterranean Holm Oak Forest
by Claudia Di Bene, Loredana Canfora, Melania Migliore, Rosa Francaviglia and Roberta Farina
Forests 2024, 15(11), 2018; https://doi.org/10.3390/f15112018 (registering DOI) - 15 Nov 2024
Viewed by 234
Abstract
Forests play a key role in the global carbon (C) cycle through multiple interactions between above-ground and soil microbial communities. Deeper insights into the soil microbial composition and diversity at different spatial scales and soil depths are of paramount importance. We hypothesized that [...] Read more.
Forests play a key role in the global carbon (C) cycle through multiple interactions between above-ground and soil microbial communities. Deeper insights into the soil microbial composition and diversity at different spatial scales and soil depths are of paramount importance. We hypothesized that in a homogeneous above-ground tree cover, the heterogeneous distribution of soil microbial functional diversity and processes at the small scale is correlated with the soil’s chemical properties. From this perspective, in a typical Mediterranean holm oak (Quercus ilex L.) peri-urban forest, soil carbon dioxide (CO2) emissions were measured with soil chambers in three different plots. In each plot, to test the linkage between above-ground and below-ground communities, soil was randomly sampled along six vertical transects (0–100 cm) to investigate soil physico-chemical parameters; microbial processes, measured using Barometric Process Separation (BaPS); and structural and functional diversity, assessed using T-RFLP and qPCR Real Time analyses. The results highlighted that the high spatial variability of CO2 emissions—confirmed by the BaPS analysis—was associated with the microbial communities’ abundance (dominated by bacteria) and structural diversity (decreasing with soil depth), measured by H′ index. Bacteria showed higher variability than fungi and archaea at all depths examined. Such an insight showed the clear ecological and environmental implications of soil in the overall sustainability of the peri-urban forest system. Full article
(This article belongs to the Special Issue Soil Organic Carbon and Nutrient Cycling in the Forest Ecosystems)
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Figure 1
<p>Daily mean air temperature monitored in the 0–24 h (°C) (shown as black continuous line), daily mean air temperature monitored at the time of soil CO<sub>2</sub> emissions measurements between 10 and 14 h (°C) (shown as black dotted line), and daily total rainfall (mm) (shown as gray column) over the soil CO<sub>2</sub> emissions monitoring period at the Castelporziano Reserve (Rome, Italy). A period was considered “dry” when the rainfall was equal to or less than twice the mean temperature (<b>a</b>). Daily mean soil temperature (°C) (shown as black dashed line) and daily mean soil water content (%, <span class="html-italic">v</span>:<span class="html-italic">v</span>) (shown as black continuous line) measured at 10 cm and 100 cm soil depth, respectively, over the soil CO<sub>2</sub> emissions monitoring period. Black and white circles represent daily mean soil temperature and daily mean water content, respectively, monitored at the time of soil CO<sub>2</sub> emissions measurements between 10 and 14 h (°C). (<b>b</b>) Soil CO<sub>2</sub> emissions (µmol CO<sub>2</sub> m<sup>−2</sup> s<sup>−1</sup>) were measured at the site in three plots (shown as plot 1: black triangle plot 2: white circle and plot 3: white diamond) during the period 6 June to 20 November 2013 with weekly or monthly soil CO<sub>2</sub> emissions monitoring (<span class="html-italic">n</span> = 12). Values are means ± SE (showed as vertical bars) of three replicates for each plot. For each measuring date, statistically significant differences among plots are shown by asterisks according to ANOVA (<span class="html-italic">* p</span> &lt; 0.05) (<b>c</b>).</p>
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<p>BaPS parameters measured at 0–20 cm layer: soil respiration rate (<span class="html-italic">RS</span>; mg C kg<sup>−1</sup> h<sup>−1</sup>) (<b>a</b>), gross denitrification rate (<span class="html-italic">Denitr</span>; µg N kg<sup>−1</sup> h<sup>−1</sup>) (<b>b</b>), and gross nitrification rate (<span class="html-italic">Nitr</span>; µg N kg<sup>−1</sup> h<sup>−1</sup>) (<b>c</b>). Values are means ± SE (showed as vertical bars) of three replicates for each plot. <span class="html-italic">Denitr</span> rate was detected in plots 1–2, while <span class="html-italic">Nitr</span> rate was only detected in plot 3. Values not followed by the same small letter are significantly different among plots within the same soil depth, according to ANOVA (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>BaPS parameters measured at 0–20 cm layer: soil respiration rate (<span class="html-italic">RS</span>; mg C kg<sup>−1</sup> h<sup>−1</sup>) (<b>a</b>), gross denitrification rate (<span class="html-italic">Denitr</span>; µg N kg<sup>−1</sup> h<sup>−1</sup>) (<b>b</b>), and gross nitrification rate (<span class="html-italic">Nitr</span>; µg N kg<sup>−1</sup> h<sup>−1</sup>) (<b>c</b>). Values are means ± SE (showed as vertical bars) of three replicates for each plot. <span class="html-italic">Denitr</span> rate was detected in plots 1–2, while <span class="html-italic">Nitr</span> rate was only detected in plot 3. Values not followed by the same small letter are significantly different among plots within the same soil depth, according to ANOVA (<span class="html-italic">p</span> &lt; 0.05).</p>
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<p>Abundance of bacteria, archaea, and fungi expressed as gene copy numbers (g<sup>−1</sup> of soil dry weight) as detected along the investigated soil depth profile (0–100 cm) in each plot (bacteria as blue line and dots, archaea as red line and dots, and fungi as green line and dots). The abundance of each microbial community represents the average value of duplicate quantifications using 16S rDNA q-PCR analysis. Gene copy numbers were expressed in scientific notation. 0E+00 and 6E+13 refer to numbers ranging from 5.83 × 10<sup>8</sup> to 5.40 × 10<sup>13</sup>.</p>
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<p>Vertical changes in numbers of bacteria, archaea, and fungi phylotypes detected along the investigated soil depth in each plot (bacteria as blue dots, archaea as red squares, and fungi as green triangles). The number of phylotypes corresponds to the number of bands on the T-RFLP profiles.</p>
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<p>Dendrograms show similarity of T-RFLP profiles using Bray–Curtis hierarchical cluster analysis along the investigated soil depth in each plot.</p>
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<p>Boxplots of diversity index (Shannon index; <span class="html-italic">H′</span>). Three different soil layers (i.e., SL, superficial layer; IL, intermediate layer; and DL, deeper layer) were discriminated according to an arbitrary analysis of soil profile. Diversity was calculated from the number and the relative peak area of bands on the T-RFLP profiles.</p>
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<p>Principal component analysis (PCA) biplot was based on soil chemical and physical parameters (pH; SOC: soil organic carbon concentration; TN: total nitrogen concentration; C/N ratio; SWC: soil water content; Soil Temp: soil temperature), microbial processes <span class="html-italic">(Rs</span>: soil respiration; <span class="html-italic">Denitr</span>: denitrification rate; <span class="html-italic">Nitr</span>: gross nitrification rate), soil CO<sub>2</sub> emissions (measured using survey soil respiration chamber), microbial abundance (<span class="html-italic">Arch</span>: Archaea abundance; <span class="html-italic">Bact</span>: bacteria abundance; <span class="html-italic">Fungi</span>: fungi abundance) and Shannon index (Arch <span class="html-italic">H′</span>: Archaea Shannon index; Bact <span class="html-italic">H′</span>: Bacteria Shannon index; Fungi <span class="html-italic">H′</span>: Fungi Shannon index). All such parameters were used as variables, while replicate plots were used as observations in the 0–20 cm soil depth. Soil chemical and physical variables are shown by black continuous arrows, microbial processes and soil CO<sub>2</sub> emissions are shown by grey heavy dotted arrows, microbial <span class="html-italic">H’</span> is shown by black heavy dotted arrows, and microbial abundance is shown by light dotted arrows. Observations are represented by black stars (plot 1), white triangles (plot 2), and white squares (plot 3). PC 1 and PC 2 axes together accounted for 77.78% of the variability and were significant (<span class="html-italic">p</span> &lt; 0.05) (<b>a</b>). PCA biplot was based on soil chemical parameters, microbial abundance, and <span class="html-italic">H’</span>, which were used as variables, while soil depths were considered as observations. Observations (10: 0–10 cm, 20:10–20 cm, 40: 20–40 cm, 60: 40–60 cm, 80: 60–80 cm, 100: 80–100 cm) are represented by black circles. In plot 1, the PC 1 and PC 2 axes together accounted for 76.04% of the variability and were significant (<span class="html-italic">p</span> &lt; 0.05) (<b>b</b>); in plot 2, the PC 1 and PC 2 axes together accounted for 81.22% of the variability and were significant (<span class="html-italic">p</span> &lt; 0.05) (<b>c</b>); in plot 3, the PC 1 and PC 2 axes together accounted for 82.84% of the variability and were significant (<span class="html-italic">p</span> &lt; 0.05) (<b>d</b>).</p>
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<p>Principal component analysis (PCA) biplot was based on soil chemical and physical parameters (pH; SOC: soil organic carbon concentration; TN: total nitrogen concentration; C/N ratio; SWC: soil water content; Soil Temp: soil temperature), microbial processes <span class="html-italic">(Rs</span>: soil respiration; <span class="html-italic">Denitr</span>: denitrification rate; <span class="html-italic">Nitr</span>: gross nitrification rate), soil CO<sub>2</sub> emissions (measured using survey soil respiration chamber), microbial abundance (<span class="html-italic">Arch</span>: Archaea abundance; <span class="html-italic">Bact</span>: bacteria abundance; <span class="html-italic">Fungi</span>: fungi abundance) and Shannon index (Arch <span class="html-italic">H′</span>: Archaea Shannon index; Bact <span class="html-italic">H′</span>: Bacteria Shannon index; Fungi <span class="html-italic">H′</span>: Fungi Shannon index). All such parameters were used as variables, while replicate plots were used as observations in the 0–20 cm soil depth. Soil chemical and physical variables are shown by black continuous arrows, microbial processes and soil CO<sub>2</sub> emissions are shown by grey heavy dotted arrows, microbial <span class="html-italic">H’</span> is shown by black heavy dotted arrows, and microbial abundance is shown by light dotted arrows. Observations are represented by black stars (plot 1), white triangles (plot 2), and white squares (plot 3). PC 1 and PC 2 axes together accounted for 77.78% of the variability and were significant (<span class="html-italic">p</span> &lt; 0.05) (<b>a</b>). PCA biplot was based on soil chemical parameters, microbial abundance, and <span class="html-italic">H’</span>, which were used as variables, while soil depths were considered as observations. Observations (10: 0–10 cm, 20:10–20 cm, 40: 20–40 cm, 60: 40–60 cm, 80: 60–80 cm, 100: 80–100 cm) are represented by black circles. In plot 1, the PC 1 and PC 2 axes together accounted for 76.04% of the variability and were significant (<span class="html-italic">p</span> &lt; 0.05) (<b>b</b>); in plot 2, the PC 1 and PC 2 axes together accounted for 81.22% of the variability and were significant (<span class="html-italic">p</span> &lt; 0.05) (<b>c</b>); in plot 3, the PC 1 and PC 2 axes together accounted for 82.84% of the variability and were significant (<span class="html-italic">p</span> &lt; 0.05) (<b>d</b>).</p>
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19 pages, 15862 KiB  
Article
Study on the Mechanical Properties and Basic Elastic Constants of Yunnan Dendrocalamus sinicus Chia et J. L. Sun
by Fengwei Zhou, Xingyu Wang, Yanrong Wang, Guofu Li and Chunlei Dong
Forests 2024, 15(11), 2017; https://doi.org/10.3390/f15112017 (registering DOI) - 15 Nov 2024
Viewed by 307
Abstract
Yunnan Dendrocalamus sinicus Chia et J. L. Sun (YDS) is a giant bamboo species with a diameter at breast height of up to nearly 40 cm. It is endemic to Yunnan, China, and only a very small portion of it is directly used [...] Read more.
Yunnan Dendrocalamus sinicus Chia et J. L. Sun (YDS) is a giant bamboo species with a diameter at breast height of up to nearly 40 cm. It is endemic to Yunnan, China, and only a very small portion of it is directly used as load-bearing beams and columns in the dwellings of ethnic minorities, such as in Dai architecture. Due to the structural characteristics of its hollow and thin walls, systematic physical and mechanical property testing of this species faces significant challenges in terms of methods and means. This issue has become one of the main barriers to the realization of its large-scale industrial use. Therefore, this paper systematically tests and studies YDS’s three kinds of strength (tension, compression, and shear), modulus of elasticity, and six Poisson’s ratios with the help of digital image correlation (DIC) technology and self-created material testing methods. The (1) tensile, compressive, and shear strengths and moduli in longitudinal, radial, and chordal directions; (2) tensile strengths and moduli of bamboo green, flesh, and yellow layers in the thickness direction of the bamboo wall; and (3) six Poisson’s ratios under tensile and compressive stresses were obtained for YDS. It was also found that the tensile strength (378.8 MPa) of the green layer of YDS exceeded the yield strength (355 MPa) of 45# steel, making it a potential high-strength engineering material or fiber-reinforced material. Full article
(This article belongs to the Section Wood Science and Forest Products)
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Figure 1

Figure 1
<p>Schematic diagram of bamboo cross-section and sample preparation: (<b>a</b>) Distribution of vascular bundles in the bamboo cross-section, (<b>b</b>) Schematic diagram of sample extraction and preparation.</p>
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<p>Schematic diagram of bamboo cross-section and sample preparation: (<b>a</b>) Distribution of vascular bundles in the bamboo cross-section, (<b>b</b>) Schematic diagram of sample extraction and preparation.</p>
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<p>Basic mechanical properties of YDS test specimens: (<b>a1</b>) longitudinal, radial and chordal tensile specimens, (<b>b1</b>) longitudinal, radial and chordal compression specimens, and (<b>c1</b>) radial and chordal shear specimens, of which (<b>a2</b>–<b>c2</b>) each represent the corresponding test specimens after undergoing surface spray speckle treatment.</p>
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<p>Basic mechanical properties of YDS test specimens: (<b>a1</b>) longitudinal, radial and chordal tensile specimens, (<b>b1</b>) longitudinal, radial and chordal compression specimens, and (<b>c1</b>) radial and chordal shear specimens, of which (<b>a2</b>–<b>c2</b>) each represent the corresponding test specimens after undergoing surface spray speckle treatment.</p>
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<p>YDS tensile load-displacement curves: (<b>a</b>) longitudinal tension of bamboo green layer, (<b>b</b>) longitudinal tension of bamboo flesh layer, (<b>c</b>) longitudinal tension of bamboo yellow layer, (<b>d</b>) longitudinal tension containing bamboo green and flesh and bamboo yellow, (<b>e</b>) radial tension, (<b>f</b>) tangential tension.</p>
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<p>Typical schematic diagram and ultimate strain diagram of tensile damage of YDS: (<b>a</b>) longitudinal tensile damage specimen (bamboo green layer), (<b>b</b>) radial tensile damage specimen, (<b>c</b>) chordal tensile damage specimen.</p>
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<p>Compression load-displacement curves of YDS: (<b>a</b>) longitudinal compression, (<b>b</b>) radial compression, (<b>c</b>) tangential compression.</p>
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<p>Typical damage schematic and ultimate strain diagram of YDS in compression: (<b>a</b>) longitudinal compression, (<b>b</b>) tangential compression, (<b>c</b>) radial compression.</p>
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<p>Radial and tangential shear load-displacement curves and damage typical diagrams and ultimate strain diagrams of YDS: (<b>a</b>,<b>c</b>) radial shear, (<b>b</b>,<b>d</b>) tangential shear.</p>
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<p>Longitudinal tensile stress-strain of YDS: (<b>a</b>) stress-strain of bamboo green layer (<span class="html-italic">LT</span>), (<b>b</b>) stress-strain of bamboo flesh layer (<span class="html-italic">LT</span>), (<b>c</b>) stress-strain of bamboo yellow layer (<span class="html-italic">LT</span>), and (<b>d</b>) stress-strain of the layer containing bamboo green, flesh, and yellow (<span class="html-italic">LR</span>). The gray dashed line in the figure represents the strain zero line, and subsequent representations will be the same.</p>
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<p>Radial tensile stress-strain of YDS: (<b>a</b>) radial section (<span class="html-italic">RL</span>), (<b>b</b>) transverse section (<span class="html-italic">RT</span>).</p>
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<p>YDS chordal tensile stress-strain: (<b>a</b>) tangential section (<span class="html-italic">TL</span>), (<b>b</b>) transverse section (<span class="html-italic">TR</span>).</p>
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<p>Longitudinal compressive stress-strain of YDS: (<b>a</b>) bamboo green tangential section (<span class="html-italic">LTO</span>) stress-strain, (<b>b</b>) bamboo yellow tangential section <span class="html-italic">(LTI</span>) stress-strain, (<b>c</b>) radial section (<span class="html-italic">LR</span>) stress-strain.</p>
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<p>Radial compressive stress-strain of YDS: (<b>a</b>) radial section (RL) stress-strain, (<b>b</b>) transverse section (RT) stress-strain.</p>
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<p>Tangential compressive stress-strain of YDS: (<b>a</b>) tangential section of bamboo green layer (TLO), (<b>b</b>) tangential section of bamboo yellow inner layer (TLI), (<b>c</b>) radial section (TR).</p>
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<p>YDS tensile, compression and shear strength: (<b>a</b>) longitudinal tensile and longitudinal compression strength box plot, (<b>b</b>) radial and tangential tensile, tangential compression, radial and tangential shear strength box plot.</p>
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<p>Tensile and compressive modulus of elasticity and shear modulus of YDS: (<b>a</b>) longitudinal tensile and compressive modulus of elasticity box plot, (<b>b</b>) radial and tangential tensile and compressive modulus of elasticity and shear modulus box plot.</p>
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<p>Tensile and compressive Poisson’s ratios of YDS: (<b>a</b>) box line plot of Poisson’s ratio under tensile loading, (<b>b</b>) local magnification of <span class="html-italic">μ<sub>TL</sub></span> and <span class="html-italic">μ<sub>RL</sub></span> in (<b>a</b>), (<b>c</b>) box line plot of Poisson’s ratio under compressive loading, (<b>d</b>) local magnification of <span class="html-italic">μ<sub>TLO</sub></span>, <span class="html-italic">μ<sub>TLI</sub></span>, and <span class="html-italic">μ<sub>RL</sub></span> in (<b>c</b>), (<b>e</b>) comparative histogram of Poisson’s ratio under tensile and compressive Poisson’s ratio comparison histograms under loading.</p>
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<p>Tensile and compressive Poisson’s ratios of YDS: (<b>a</b>) box line plot of Poisson’s ratio under tensile loading, (<b>b</b>) local magnification of <span class="html-italic">μ<sub>TL</sub></span> and <span class="html-italic">μ<sub>RL</sub></span> in (<b>a</b>), (<b>c</b>) box line plot of Poisson’s ratio under compressive loading, (<b>d</b>) local magnification of <span class="html-italic">μ<sub>TLO</sub></span>, <span class="html-italic">μ<sub>TLI</sub></span>, and <span class="html-italic">μ<sub>RL</sub></span> in (<b>c</b>), (<b>e</b>) comparative histogram of Poisson’s ratio under tensile and compressive Poisson’s ratio comparison histograms under loading.</p>
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11 pages, 573 KiB  
Article
Concentration of Nutrients in Individual Organs of European Beech (Fagus sylvatica L.) Seedlings and Root System Development as a Result of Different Fertilization
by Michał Jasik, Karolina Staszel-Szlachta, Stanisław Małek and Jacek Banach
Forests 2024, 15(11), 2016; https://doi.org/10.3390/f15112016 (registering DOI) - 15 Nov 2024
Viewed by 185
Abstract
The large-scale dieback of spruce monocultures, especially in the lower alpine, has become a significant problem and has necessitated the restoration of these areas, mainly using seedlings produced in forest nurseries. The primary source of nutrients for seedlings can be slow-release fertilizers and [...] Read more.
The large-scale dieback of spruce monocultures, especially in the lower alpine, has become a significant problem and has necessitated the restoration of these areas, mainly using seedlings produced in forest nurseries. The primary source of nutrients for seedlings can be slow-release fertilizers and an appropriate dose of fertilizer improves the efficiency of its use and minimizes the negative environmental impact associated with the excessive use of mineral fertilizers. Aims: This study aimed to evaluate the effect of applying different fertilizer dose combinations on the accumulation of macronutrients in different parts of the seedlings (roots, shoots, and leaves) and on the morphology and development of fine roots. Methods: This research was carried out on producing beech seedlings with the application of starter soil fertilization with Yara Mila Complex (YMC) and Osmocote Exact Standard 3-4M (OES) fertilizers in four varying doses. Results: No deficiency of the analyzed macronutrients was noted in any of the tested fertilization variants. The highest content of all analyzed macronutrients was recorded in the leaves of beech seedlings, with values in roots and shoots being several times lower. The mixed fertilization variant OES 1.0 + YMC 1.0 shows a positive correlation with all analyzed elements and the parameters DQI (Dickson Quality Index), SA (Surface Area), RV (Root Volume), and mass. Conclusion: Results confirm the hypothesis that applying a mixture of fast-acting (YMC) and slow-acting (OES) fertilizer positively affects the nutrition and accumulation of macronutrients and the development of root systems in beech seedlings compared to fertilization with a single fertilizer. Full article
(This article belongs to the Section Forest Ecophysiology and Biology)
14 pages, 3218 KiB  
Article
Reconstruction of Minimum May Temperatures in Northeast China Since 1797 AD Based on Tree Ring Width in Pinus sylvestris var. mongolica
by Xinrui Wang, Zhaopeng Wang, Muxiao Liu, Dongyou Zhang, Taoran Luo, Xiangyou Li, Bingyun Du, Yang Qiu, Linlin Li and Yueru Zhao
Forests 2024, 15(11), 2015; https://doi.org/10.3390/f15112015 (registering DOI) - 15 Nov 2024
Viewed by 217
Abstract
We developed a tree ring width chronology from 1797 to 2020 (224 years) for the northwestern foothills of the Greater Khingan Mountains (GKMs) in northeastern China using 51 tree ring sample cores from 24 Pinus sylvestris var. mongolica (PSM). Pearson’s correlation analysis [...] Read more.
We developed a tree ring width chronology from 1797 to 2020 (224 years) for the northwestern foothills of the Greater Khingan Mountains (GKMs) in northeastern China using 51 tree ring sample cores from 24 Pinus sylvestris var. mongolica (PSM). Pearson’s correlation analysis was used to analyze the relationship between tree ring width and regional climate factors. The standardized chronology was positively associated with the minimum temperature (Tmin) in the previous May (r = 0.721, p < 0.01), indicating that this parameter was the main climatic factor limiting PSM growth in the region. We established a secure reconstruction equation for the May Tmin from 1797 to 2020. There were 31 warm and 43 cold years in the 224-year reconstructed temperature series, accounting for 13.8% and 19.2% of the total years, respectively. Warm periods were observed in 1820–1829, 1877–1898, 1947–1958, and 1991–2020, whereas cold periods occurred in 1820, 1829–1870, 1899–1927, 1934–1947, and 1960–1988. The observed temperature sequence was highly consistent with the reconstructed sequence from the tree rings, which verified the reliability of the reconstructed results. The spatial correlation analysis indicated that the reconstructed temperature sequence accurately represented the temperature changes in the northwestern foothills of the GKM and surrounding areas. Multi-window spectral analysis and wavelet analysis revealed significant periodic fluctuations from 2 to 6 years, 21.2 years, 48.5 years, and 102.2 years. These periodic variations may be related to the El Niño–Southern Oscillation (ENSO), the Atlantic Multi-Year Intergenerational Oscillation (AMO), the Pacific Decadal Oscillation (PDO), and solar activity. This study expands the existing climate records in the region and provides valuable data support for understanding climate change patterns in the GKM and the scientific predictions of future climate changes. Full article
(This article belongs to the Section Forest Ecology and Management)
19 pages, 6815 KiB  
Article
Vegetation Recovery Patterns at Jeongseon Alpine Stadium, Mount Gariwang, in the Republic of Korea, After the PyeongChang 2018 Winter Olympics
by Su-Won Lee, Jeong-Eun Lee, Ju-Hyeon Song and Chung-Weon Yun
Forests 2024, 15(11), 2014; https://doi.org/10.3390/f15112014 - 15 Nov 2024
Viewed by 243
Abstract
This study assessed vegetation recovery at Jeongseon Alpine Stadium, Mt. Gariwang, 5 years after the 2018 PyeongChang Winter Olympics to aid in restoration planning. A total of 50 quadrats were surveyed across undisturbed areas, forest edges, and damaged areas at different altitudes. Species [...] Read more.
This study assessed vegetation recovery at Jeongseon Alpine Stadium, Mt. Gariwang, 5 years after the 2018 PyeongChang Winter Olympics to aid in restoration planning. A total of 50 quadrats were surveyed across undisturbed areas, forest edges, and damaged areas at different altitudes. Species occurrences were recorded using a tabulation method to identify characteristic and differential species based on disturbance type. Importance value analysis showed that tree layers were present only in undisturbed areas at all altitudes, while shade-intolerant species, such as Amur choke cherry (P. glandulifolia), had high importance in the subtree layer in low-altitude damaged areas and mid-altitude forest edges. Species diversity was higher in forest edges at medium and high altitudes, whereas control areas exhibited higher diversity at low altitudes. DCA ordination revealed distinct community groupings based on altitude and disturbance type, indicating community heterogeneity. The study found rapid vegetation recovery in damaged areas and forest edges, driven by shade-intolerant species. Restoration efforts should prioritize these species to support successful recovery. Full article
(This article belongs to the Section Forest Ecology and Management)
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<p>Maps showing the study location and sites. (<b>a</b>) Mt. Gariwang and Baekdudaegan (a mountain stream extending from Mt. Baekdu, North Korea, to Mt. Jiri, South Korea). (<b>b</b>) Three study sites on the Jeongseon Alpine Stadium slope: Ⓐ low-altitude, Ⓑ mid-altitude, and Ⓒ high-altitude study sites.</p>
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<p>Climate diagram of Bukpyeong in Jeongseon, located approximately 10 km away from the study site [<a href="#B27-forests-15-02014" class="html-bibr">27</a>].</p>
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<p>Cross-section (A–A′ in <a href="#forests-15-02014-f001" class="html-fig">Figure 1</a>) of the vertical vegetation structure at the low-altitude site.</p>
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<p>Cross-section (B–B′ in <a href="#forests-15-02014-f001" class="html-fig">Figure 1</a>) of the vertical structure at the middle altitude site.</p>
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<p>Cross-section (C–C′ in <a href="#forests-15-02014-f001" class="html-fig">Figure 1</a>) of the vertical vegetation structure at the high-altitude site.</p>
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<p>Detrended correspondence analysis ordination according to altitude and disturbance types.</p>
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<p>The mechanisms of secondary succession following five years after an ecosystem disturbance. The red text represents shade-intolerant species.</p>
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13 pages, 651 KiB  
Article
Influence or Interference? Understanding Crowding Effects in Forest Management Adoption
by Bindu Paudel, Jean Fritz Saint Preux, Benjamin David Wegener and Mo Zhou
Forests 2024, 15(11), 2013; https://doi.org/10.3390/f15112013 - 15 Nov 2024
Viewed by 209
Abstract
More than half of the private forestland in the U.S. is under non-industrial private forest (NIPF) ownership. Understanding NIPF landowners’ decision-making is crucial for developing effective policy that promotes sustainable forest management practices and ensures forest health. This study investigates the factors influencing [...] Read more.
More than half of the private forestland in the U.S. is under non-industrial private forest (NIPF) ownership. Understanding NIPF landowners’ decision-making is crucial for developing effective policy that promotes sustainable forest management practices and ensures forest health. This study investigates the factors influencing the adoption of different management practices, with a focus on potential crowding effects among these practices. Drawing on data from over four hundred NIPF landowners in the U.S. central hardwood region, a series of binary logistic regression models were employed to analyze the relationship between landowner and forestland characteristics and the likelihood of adopting various management practices, like invasive plant management, forest stand improvement, and grapevine control. The findings reveal that factors, such as forest acreage, proximity of landowner residence to the forest, and education level, significantly affect the likelihood of adopting management practices. More importantly, this study found evidence of crowding-in effects, where implementing one practice increased the probability of adopting others, suggesting a preference among NIPF landowners for a diverse approach to forest management. Full article
(This article belongs to the Section Forest Economics, Policy, and Social Science)
19 pages, 2293 KiB  
Article
Fungal Diversity in Fire-Affected Pine Forest Soils at the Upper Tree Line
by Jelena Lazarević, Ana Topalović and Audrius Menkis
Forests 2024, 15(11), 2012; https://doi.org/10.3390/f15112012 - 15 Nov 2024
Viewed by 221
Abstract
Forest fires represent a significant ecological disturbance in ecosystems that increasingly affects Pinus heldreichii H. Christ forests at the upper tree line in Montenegro, due to climate change and anthropogenic factors. Soil samples were collected from five high-altitude sites in the Kuči Mountains, [...] Read more.
Forest fires represent a significant ecological disturbance in ecosystems that increasingly affects Pinus heldreichii H. Christ forests at the upper tree line in Montenegro, due to climate change and anthropogenic factors. Soil samples were collected from five high-altitude sites in the Kuči Mountains, including three post-fire sites (2-, 4-, and 6-years post-fire) and two unburned control sites. High-throughput sequencing and soil chemical analyses were conducted to assess fungal diversity, community composition, and soil nutrient properties. The results showed that fungal diversity was significantly higher in unburned soils compared to post-fire soils, with the most prominent changes in ectomycorrhizal fungi, which are crucial for pine regeneration. The fungal community composition differed markedly between the post-fire and unburned sites, with specific taxa such as Hygrocybe conica (Schaeff.) P. Kumm. and Solicoccozyma aeria (Saito) Yurkov dominating the post-fire environments. Despite this, the fungal richness did not significantly change over time (2-, 4-, or 6-years post-fire), suggesting the slow recovery of fungal communities in high-altitude environments. In addition to shifts in fungal biodiversity, the post-fire soils exhibited higher levels of available phosphorus, likely due to the conversion of organic phosphorus into soluble forms during combustion. However, the organic matter content remained unchanged. This study provided important insights into the long-term ecological impacts of forest fires on high-altitude P. heldreichii forests and underlined the importance of preserving unburned forest areas to maintain fungal biodiversity and support natural regeneration, as well as the potential need for active restoration strategies in fire-affected regions. Full article
(This article belongs to the Section Natural Hazards and Risk Management)
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<p>Fire-destroyed <span class="html-italic">Pinus heldreichii</span> forest stands at the upper tree line at the Hum Orahovski site in Montenegro.</p>
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<p>Hierarchical clustering dendrogram on physical and chemical soil properties in post-fire and unburned forest sites. Site names are shown in parentheses: T—Treskavac; K—Kastrat; HO—Hum Orahovski; KK—Kučka Korita; and S—Sovrh.</p>
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<p>Venn diagram showing unique and shared OTUs among different groups of samples. Within each group, data from different sites is combined. The size of each circle represents the number of unique OTUs. Roolets (blue), Unburned soil (green), post-fire soil (red).</p>
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<p>Bar chart showing the relative abundance of different fungal classes. Classes that accounted for less than 1% of the total fungal community were combined into an Other category.</p>
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<p>Ordination diagram based on detrended correspondence analysis of fungal communities from post-fire forest soil (square), unburned forest soil (circle), and rootlets of <span class="html-italic">Pinus heldreichii</span> from unburned forest stands (diamonds). Size of each plot shows relative richness of fungal OTUs. Site names are shown in parentheses: T—Treskavac; K—Kastrat; HO—Hum Orahovski; KK—Kučka Korita; and S—Sovrh. In ordination, 21.6% of variation was explained on <span class="html-italic">x</span>-axis, and 9.7% on <span class="html-italic">y</span>-axis.</p>
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<p>A cluster map of the 10 most common fungal OTUs across various soil and root samples. The dendrograms illustrate the hierarchical relationships among the OTUs and the samples based on their abundance profiles.</p>
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12 pages, 1647 KiB  
Article
Dendroclimatic Response of Jack Pine (Pinus banksiana) Affected by Shoot Blight Caused by Diplodia pinea
by Sophan Chhin and Kaelyn Finley
Forests 2024, 15(11), 2011; https://doi.org/10.3390/f15112011 - 15 Nov 2024
Viewed by 252
Abstract
The overall objective of our study was to examine the influence of climatic factors and tree-based competition on the radial growth of jack pine (Pinus banksiana) forests affected by the fungal pathogen, Diplodia pinea. Our study utilized dendroclimatic techniques to [...] Read more.
The overall objective of our study was to examine the influence of climatic factors and tree-based competition on the radial growth of jack pine (Pinus banksiana) forests affected by the fungal pathogen, Diplodia pinea. Our study utilized dendroclimatic techniques to examine how past annual diameter growth can be influenced by the historical climate of the region. Twenty jack pine sites were sampled in Michigan within the Upper Peninsula (UP) and the Lower Peninsula (LP) region. Furthermore, two condition levels of forest health (D. pinea-affected vs. healthy reference stands) were considered between two levels of stand density (i.e., high vs. low density). The relationships between radial growth and climate identified in this study indicated that jack pine radial growth was typically affected by the climatic moisture index, whereas the response to temperature variables was weak to non-existent. In the Upper Peninsula region, crown damage likely sustained during harsh winters could have made jack pine stands prone to D. pinea by facilitating a point of entry for infection; furthermore, higher-density stands infected by D. pinea were influenced by moisture stress that occurred during the summer of the prior year. In the LP region, regardless of stand density, D. pinea was sensitive to moisture stress in the summer of the prior growing season; furthermore, negative relationships with precipitation in the spring may have improved spore dispersion in D. pinea-affected stands. Overall, our study provides improved understanding of the interactive role of climatic stress and forest pathogens on jack pine productivity. Full article
(This article belongs to the Special Issue Impact of Pests, Climate and Other Factors on Forest Health)
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<p>The study was conducted in Huron National Forest in the Lower Peninsula region and in Hiawatha National Forest in the Upper Peninsula region of Michigan (MI). Note: National Forests are indicated by dark gray shading.</p>
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<p>Chronologies of jack pine growth based on sampling in Michigan’s (<b>a</b>) Upper Peninsula region and (<b>b</b>) Lower Peninsula region for 1986–2011. Treatment group abbreviations are as follows: UP = Upper Peninsula region, LP = Lower Peninsula region, R = reference stands that are healthy, D = <span class="html-italic">Diplodia</span> present, L = low density, H = high density.</p>
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<p>Chronologies of jack pine growth based on sampling in Michigan’s (<b>a</b>) Upper Peninsula region and (<b>b</b>) Lower Peninsula region for 1986–2011. Treatment group abbreviations are as follows: UP = Upper Peninsula region, LP = Lower Peninsula region, R = reference stands that are healthy, D = <span class="html-italic">Diplodia</span> present, L = low density, H = high density.</p>
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<p>Jack pine growth responses to monthly and 3-month seasonal (<b>a</b>) mean temperature and (<b>b</b>) climate moisture index. In each regression model, lighter gray boxes highlight climatic variables as having a positive association with radial growth, while darker gray boxes showcase climatic variables as having a negative association with radial growth. All climatic relationships presented in each model are significant statistically (<span class="html-italic">p</span> &lt; 0.05). Treatment group abbreviations are as follows: UP = Upper Peninsula of Michigan, LP = Lower Peninsula of Michigan, R = reference sites that are healthy, D = <span class="html-italic">Diplodia</span>-present, L = low density, H = high density. For treatment groups that have more than 1 significant climate variable in the regression model, these variables in turn were ranked, and variables ranked as 1 had the strongest influence on radial growth.</p>
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19 pages, 4707 KiB  
Article
Chlorophyll Content Estimation of Ginkgo Seedlings Based on Deep Learning and Hyperspectral Imagery
by Zilong Yue, Qilin Zhang, Xingzhou Zhu and Kai Zhou
Forests 2024, 15(11), 2010; https://doi.org/10.3390/f15112010 - 14 Nov 2024
Viewed by 373
Abstract
Accurate estimation of chlorophyll content is essential for understanding the growth status and optimizing the cultivation practices of Ginkgo, a dominant multi-functional tree species in China. Traditional methods based on chemical analysis for determining chlorophyll content are labor-intensive and time-consuming, making them [...] Read more.
Accurate estimation of chlorophyll content is essential for understanding the growth status and optimizing the cultivation practices of Ginkgo, a dominant multi-functional tree species in China. Traditional methods based on chemical analysis for determining chlorophyll content are labor-intensive and time-consuming, making them unsuitable for large-scale dynamic monitoring and high-throughput phenotyping. To accurately quantify chlorophyll content in Ginkgo seedlings under different nitrogen levels, this study employed a hyperspectral imaging camera to capture canopy hyperspectral images of seedlings throughout their annual growth periods. Reflectance derived from pure leaf pixels of Ginkgo seedlings was extracted to construct a set of spectral parameters, including original reflectance, logarithmic reflectance, and first derivative reflectance, along with spectral index combinations. A one-dimensional convolutional neural network (1D-CNN) model was then developed to estimate chlorophyll content, and its performance was compared with four common machine learning methods, including Gaussian Process Regression (GPR), Partial Least Squares Regression (PLSR), Support Vector Regression (SVR), and Random Forest (RF). The results demonstrated that the 1D-CNN model outperformed others with the first derivative spectra, achieving higher CV-R2 and lower RMSE values (CV-R2 = 0.80, RMSE = 3.4). Furthermore, incorporating spectral index combinations enhanced the model’s performance, with the 1D-CNN model achieving the best performance (CV-R2 = 0.82, RMSE = 3.3). These findings highlight the potential of the 1D-CNN model in strengthening the chlorophyll estimations, providing strong technical support for the precise cultivation and the fertilization management of Ginkgo seedlings. Full article
(This article belongs to the Section Forest Inventory, Modeling and Remote Sensing)
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<p>The workflow for estimating chlorophyll content in <span class="html-italic">Ginkgo</span> canopies based on hyperspectral imaging and 1D-CNN.</p>
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<p>Schematic representation of the experimental layout for <span class="html-italic">Ginkgo biloba</span> seedlings under five nitrogen treatments (N0–N4). Each treatment was replicated three times (R1–R3), resulting in 15 experimental units in total. Nitrogen was applied as a topdressing in three equal doses during the growing season.</p>
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<p>Hyperspectral images of <span class="html-italic">Ginkgo biloba</span> seedlings under different nitrogen levels (N0–N4) across growth stages (T1–T5). T1 corresponds to April (early bud development stage), T2 corresponds to May (early rapid growth stage), T3 corresponds to June (middle rapid growth stage), T4 corresponds to July (late rapid growth stage), and T5 corresponds to August (plant maturity stage).</p>
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<p>A suitable 1D-CNN model for spectral reflectance is proposed.</p>
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<p>Changes in canopy reflectance and SPAD chlorophyll content of <span class="html-italic">Ginkgo</span> seedlings across different growth stages and nitrogen fertilization levels (<b>A</b>) Spectral reflectance curves of the <span class="html-italic">Ginkgo</span> canopy at different SPAD levels. The figure includes three forms of reflectance spectra: (i) original reflectance, (ii) logarithmic reflectance, and (iii) first derivative reflectance. SPAD chlorophyll content is divided into low (SPAD_low), medium (SPAD_medium), and high (SPAD_high) levels. Low SPAD corresponds to values from 27 to 45, medium SPAD ranges between 45 and 55, and high SPAD corresponds to values from 55 to 65. Reflectance across the 400 to 900 nm range varies with SPAD levels, reflecting the sensitivity of different spectral regions to chlorophyll absorption and canopy structure. (<b>B</b>) Changes in SPAD chlorophyll content of <span class="html-italic">Ginkgo</span> seedlings at different growth stages (T1–T5). T1 represents April (early bud development stage), T2 represents May (early rapid growth stage), T3 represents June (middle rapid growth stage), T4 represents July (late rapid growth stage), and T5 represents August (plant maturity stage). SPAD content fluctuates across the different growth stages. (<b>C</b>) Changes in SPAD chlorophyll content of <span class="html-italic">Ginkgo</span> seedlings under different nitrogen fertilization treatments (N0–N4). SPAD content shows significant variation across the different nitrogen levels.</p>
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<p>Correlation coefficient curve between leaf SPAD-chlorophyll content in <span class="html-italic">Ginkgo</span> seedlings and original or transformed reflectance spectra.</p>
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<p>The correlation between leaf chlorophyll content and the three best-performing indices: SR<sub>708,775</sub>, GNDVI, and mCI<sub>Green</sub>.</p>
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<p>Optimal reflectance datasets for the correlation of DVI<sub>log</sub> ((<b>A</b>), logarithmic reflectance), RVI<sub>FD</sub> ((<b>B</b>), first derivative of reflectance), NDVI<sub>FD</sub> ((<b>C</b>), first derivative of reflectance), and mRVI<sub>log</sub> ((<b>D</b>), logarithmic reflectance) with chlorophyll content. The white arrow indicates the optimal band combination.</p>
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<p>Comparison of predicted versus measured SPAD values for <span class="html-italic">Ginkgo</span> seedling canopies using various modeling approaches. Best Spectrum-Orgi, Best Spectrum-log and Best Spectrum-FD represent the best-performing spectral data (Orgi: original spectra; log: logarithmic spectra; FD: first-derivative spectra) for each regression method. VI represents vegetation indices.</p>
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13 pages, 4299 KiB  
Article
Coarse Woody Debris Dynamics in Relation to Disturbances in Korea’s Odaesan National Park Cool-Temperate Forests
by Kyungeun Lee and Yeonsook Choung
Forests 2024, 15(11), 2009; https://doi.org/10.3390/f15112009 - 14 Nov 2024
Viewed by 267
Abstract
Coarse woody debris (CWD) has historically been extensively utilized in Korea, with significant accumulation occurring mainly after the establishment of protected areas. This study, conducted in Odaesan National Park (designated in 1975), investigated the distribution and characteristics of CWD across five forest types [...] Read more.
Coarse woody debris (CWD) has historically been extensively utilized in Korea, with significant accumulation occurring mainly after the establishment of protected areas. This study, conducted in Odaesan National Park (designated in 1975), investigated the distribution and characteristics of CWD across five forest types with permanent plots. It also examined the effects of human and natural disturbances on CWD dynamics and evaluated its role in carbon storage. CWD mass varied significantly, ranging from 0.7 Mg ha−1 in Pinus-Quercus (PQ) forests to 31.9 Mg ha−1 in Broadleaved–Abies (BA) forests. The impacts of disturbances shifted markedly before and after the park’s designation; prior to this, human activities such as logging substantially affected BA, PQ, and Prunus-Salix (PS) forests, while Quercus-Tilia (QT) forests were primarily impacted by wildfires. After designation, natural disturbances became the primary contributors to CWD accumulation, with a major windstorm in BA forests adding 12.09 Mg ha−1 of CWD (37.8% of the total). Late-successional forests exhibited higher CWD mass, advanced decay stages, and greater diversity, as well as elevated CWD-to-carbon storage ratios, highlighting their role as crucial carbon reservoirs. In light of climate change, these findings emphasize the need for forest management practices that enhance CWD’s contributions to biodiversity conservation and carbon storage. Full article
(This article belongs to the Section Forest Ecology and Management)
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<p>Stump cut by logging (<b>left</b>) and tree uprooted by the windstorm in 2006 (<b>right</b>).</p>
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<p>Examples of decay class (<b>1</b> to <b>5</b>) for <span class="html-italic">Acer pseudo-sieboldianum</span> logs.</p>
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<p>Types, size, and decay state of CWD across five forest types in 2008. BA* is the value of BA’s CWD mass excluding the CWD caused by the 2006 strong windstorm. PQ: <span class="html-italic">Pinus-Quercus</span> forest, QT: <span class="html-italic">Quercus-Tilia</span> forest, BA: Broadleaved–<span class="html-italic">Abies</span> mixed forest, PS: <span class="html-italic">Populus-Salix</span> forest, SA: Subalpine forest.</p>
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<p>CWD mass (<b>a</b>) and CWD diversity index (<b>b</b>) according to forest succession stage. PQ: <span class="html-italic">Pinus-Quercus</span> forest, QT: <span class="html-italic">Quercus-Tilia</span> forest, BA: Broadleaved–<span class="html-italic">Abies</span> mixed forest, PS: <span class="html-italic">Populus-Salix</span> forest, SA: Subalpine forest.</p>
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<p>Carbon storage of the forest living trees and CWD (Mg ha<sup>−1</sup>) (<b>a</b>) and their proportion (<b>b</b>) by forest type. BA* is the value of BA’s CWD mass excluding the CWD caused by the 2006 strong windstorm. PQ: <span class="html-italic">Pinus-Quercus</span> forest, QT: <span class="html-italic">Quercus-Tilia</span> forest, BA: Broadleaved–<span class="html-italic">Abies</span> mixed forest, PS: <span class="html-italic">Populus-Salix</span> forest, SA: Subalpine forest.</p>
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<p>Plot-level biomass changes (DBH ≥ 10 cm) over a ten-year period (2005–2015). PQ: <span class="html-italic">Pinus-Quercus</span> forest, QT: <span class="html-italic">Quercus-Tilia</span> forest, BA: Broadleaved–<span class="html-italic">Abies</span> mixed forest, PS: <span class="html-italic">Populus-Salix</span> forest, SA: Subalpine forest. A paired <span class="html-italic">t</span>-test was performed between the start and end of the 10-year interval within a forest type at * <span class="html-italic">p</span> &lt; 0.05.</p>
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28 pages, 12916 KiB  
Article
Road Landscape Design: Harmonious Relationship Between Ecology and Aesthetics
by Mingqian Si, Yan Mu and Youting Han
Forests 2024, 15(11), 2008; https://doi.org/10.3390/f15112008 - 14 Nov 2024
Viewed by 255
Abstract
In view of global climate and environmental challenges, exploring sustainable urban vegetation management and development is crucial. This study aims to investigate the design strategies of urban road green space plants under the guidance of the dual theories of carbon sequestration and cooling [...] Read more.
In view of global climate and environmental challenges, exploring sustainable urban vegetation management and development is crucial. This study aims to investigate the design strategies of urban road green space plants under the guidance of the dual theories of carbon sequestration and cooling eco-efficiency and aesthetics. In this study, Yangling, a representative small- and medium-sized city, was selected as the study area, and road green space plants were identified as the research objects. The assimilation method was employed to ascertain the carbon sequestration and oxygen release, as well as the cooling and humidification capacities of the plants. The aesthetic quality of the plants was evaluated using the Scenic Beauty Estimation and Landscape Character Assessment. Finally, we propose design strategies for landscapes with higher aesthetic and carbon sequestration and cooling benefits. The results demonstrate a clear nonlinear positive correlation. The carbon sequestration and cooling benefits of plants and the aesthetic quality, with correlation coefficients of 0.864 and 0.922, respectively. Across the same sample points, the rankings of standardized values for carbon sequestration, cooling benefits, and aesthetic quality vary minimally. This indicates that eco-efficient plants with harmonious colors and elegant forms can boost the aesthetic appeal and ecological function in road green spaces. Furthermore, the Sophora japonica Linn., Ligustrum lucidum Ait., Koelreuteria paniculata Laxm., Prunus serrulata Lindl., Prunus cerasifera Ehrhar f., Ligustrum sinense Lour., Photinia × fraseri Dress, Ligustrum × vicaryi Rehder, Sabina chinensis (L.) Ant. cv. Kaizuca, and Ophiopogon japonicus (L. f.) Ker Gawl. are proved to be ecologically dominant plants. They can be employed as the principal selected species for plant design. This study summarizes applicable design strategies for three types of green spaces: avenue greenbelts, traffic separation zones, and roadside greenbelts. The nonlinear regression model developed here provides a reference for scientifically assessing and optimizing urban planting designs. Full article
(This article belongs to the Section Urban Forestry)
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<p>Graphical abstract.</p>
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<p>Location of Yangling Demonstration Zone, Xianyang, Shaanxi, China.</p>
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<p>Road green space plant application frequency.</p>
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<p>Road network analysis and sample distribution in the study area.</p>
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<p>Photographs for SBE. “G” is the Grass sample points, “S” is the Shrub sample points, “TS” is the Tree/Shrub sample points, “TG” is the Tree/Grass sample points, “SG” is the Shrub/Grass sample points, “TSG” is the Tree/Shrub/Grass sample points, “Z” is the Traffic separation green zone, “R” is the Roadside greenbelt, and “A” is the Avenue greenbelt. See <a href="#app1-forests-15-02008" class="html-app">Appendix A</a> for details.</p>
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<p>In the road green space plant application frequency table, “P” is the application frequency, and “%” on A represents the percentage of the number of plants in the interval to the total number of plants.</p>
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<p>Cluster analysis of plant’s carbon sequestration and cooling value.</p>
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<p>Trend chart of sample points feature score, and “Range” is the score interval.</p>
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<p>Correlation between SBE and landscape characteristic value.</p>
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<p>Scatter plot between W<sub>C</sub>-SBI and T-SBI.</p>
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<p>The linear regression model of the SBI–ecological relationship. The simulation process is shown in <a href="#app6-forests-15-02008" class="html-app">Appendix F</a>.</p>
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<p>Standardized value ranking of SBI, W<sub>C</sub>, and T.</p>
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<p>Evaluation of population structure analysis.</p>
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<p>Scatter plot of correlation coefficient.</p>
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12 pages, 3364 KiB  
Article
Variations in Physical and Mechanical Properties Between Clear and Knotty Wood of Chinese Fir
by Yingchao Ruan, Zongming He, Shaohui Fan, Zhiyun Chen, Ming Li, Xiangqing Ma and Shuaichao Sun
Forests 2024, 15(11), 2007; https://doi.org/10.3390/f15112007 - 14 Nov 2024
Viewed by 273
Abstract
Significant market value discrepancies exist between clear and knotty Chinese fir (Cunninghamia lanceolata) wood, distinguished not only by their aesthetic variations but also by their distinct material properties. This study aimed to explore the differences in physical and mechanical properties between [...] Read more.
Significant market value discrepancies exist between clear and knotty Chinese fir (Cunninghamia lanceolata) wood, distinguished not only by their aesthetic variations but also by their distinct material properties. This study aimed to explore the differences in physical and mechanical properties between clear and knotty Chinese fir wood. Nine standard trees were chosen from a 26-year-old Chinese fir plantation for the experiment. Subsequent to felling, trunk segments below 7 m in length were transported to the laboratory. For each tree, detailed preparations were made to obtain clear and knotty wood specimens, and these distinct wood specimens were subjected to thorough physical and mechanical assessments. The results revealed significant variations in properties between clear and knotty Chinese fir wood. The shrinkage and swelling coefficients of knotty wood were generally lower than those of clear wood, except for higher radial and tangential air-dry shrinkage. Specifically, the swelling ratio of knotty wood was at least 0.40% lower, and the oven-dry shrinkage was at least 0.58% lower than that of clear wood. Knotty wood exhibited higher air-dry and oven-dry densities, with its density being at least 0.15 g cm−3 higher than that of clear wood. However, its mechanical properties, including tensile strength, compression strength, impact bending strength, bending strength, and modulus of elasticity, were lower than those of clear wood. For instance, the tensile strength parallel to the grain of clear wood was 40.63 MPa higher, the modulus of elasticity was 1595 MPa higher, and the impact bending strength was 27.12 kJ m−2 greater than that of knotty wood. Although the tangential and radial surface hardness of knotty wood increased significantly compared to clear wood, the end hardness remained relatively lower. Overall, knotty Chinese fir wood displayed enhanced physical properties, whereas clear wood showcased superior mechanical properties. Careful selection between clear and knotty wood is recommended based on the specific requirements of wooden structural elements to optimize timber resource utilization. Full article
(This article belongs to the Section Wood Science and Forest Products)
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<p>Location of Shaowu city showing the study site. (<b>A</b>) Standing trees of Chinese fir. (<b>B</b>) Logs of Chinese fir.</p>
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<p>Schematic diagram of the manufacturing process of wood specimens.</p>
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<p>Comparison of physical properties between clear and knotty wood of Chinese fir. (<b>A</b>) Swelling ratio in different directions, (<b>B</b>) shrinkage ratio in different directions, (<b>C</b>) volumetric dry shrinkage coefficient, (<b>D</b>) air-dry and oven-dry density. The presence of different lowercase letters (a or b) among the parameters indicates a significant difference; conversely, identical lowercase letters (a or b) suggest no significant difference.</p>
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<p>Comparison of mechanical properties between clear and knotty wood of Chinese fir. (<b>A</b>) Tensile strength parallel to the grain, (<b>B</b>) impact bending strength, (<b>C</b>) modulus of elasticity in bending, (<b>D</b>) bending strength, (<b>E</b>) ultimate stress in compression parallel to the grain, (<b>F</b>) static hardness in different directions. The presence of different lowercase letters (a or b) among the parameters indicates a significant difference; conversely, identical lowercase letters (a or b) suggest no significant difference.</p>
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20 pages, 6021 KiB  
Article
Identifying Superior Growth and Photosynthetic Traits in Eighteen Oak Varieties for Southwest China
by Zengzhen Qi, Xiang Huang, Yang Peng, Hongyi Wu, Zhenfeng Xu, Bo Tan, Yu Zhong, Peng Zhu, Wei Gong, Gang Chen, Xiaohong Chen and Wenkai Hui
Forests 2024, 15(11), 2006; https://doi.org/10.3390/f15112006 - 14 Nov 2024
Viewed by 286
Abstract
Quercus, commonly known as oak, has great potential as one of the most widely cultivated plant species. However, the lack of superior varieties is a bottleneck for its usage and application in Southwest China. Here, this study aims to explore the growth [...] Read more.
Quercus, commonly known as oak, has great potential as one of the most widely cultivated plant species. However, the lack of superior varieties is a bottleneck for its usage and application in Southwest China. Here, this study aims to explore the growth and photosynthetic traits of 18 oak varieties with the goal of identifying the adaptable superior varieties for the region, focusing on nutrient growth, leaf morphology, chlorophyll content, and photosynthetic parameters over a 32-week growth period. The results showed that a significant diversity was observed among the varieties. Growth rhythm and fitted curves divided the 18 oak varieties into three patterns. Additionally, for the leaf morphological parameters, Q. denta boasted the maximum leaf area (167.24 cm2), leaf width (13.62 cm), and leaf aspect ratio (156.6); Q. mongo showed the greatest leaf length (20.37 cm); while Q. acutis had the largest leaf form factor (3.44) and leaf gap (0.39). Chlorophyll content was based on three-time-points investigation, with higher levels observed in Q. mongo, Q. robur 4, Q. wutai, Q. denta, Q. acutis, and Q. robur 1. The transpiration rate (E) (5.03 mmol m−2), stomatal conductance (gsw) (0.22 mol m−2 s−1), and total water vapor conductance (gtw) (0.19 mol m−2 s−1) were dominantly obtained in Q. robur 1, while Q. denta exhibited the highest intercellular CO2 concentration (Ci) (564.67 µmol mol−1). Conversely, Q. wutai displayed a significantly higher leaf chamber CO2 concentration (Ca) (502.11 µmol mol−1). Furthermore, growth traits showed a correlation with leaf morphological and photosynthetic traits. PCA analysis grouped the oak varieties into five clusters, with Q. acutis, Q. robur 1, Q. palus 3, Q. denta, Q. nutta, Q. mongo, and Q. wutai identified as superior varieties. These findings not only offer promising oak candidate varieties for Southwest China, but also provide insights for establishing efficient breeding program for other woody plants. Full article
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<p>The average growth patterns of seedling height (<b>a</b>) and ground diameter (<b>b</b>) across the annual growing season for 18 oak varieties.</p>
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<p><b>Primary patterns of growth rhythm in oak seedling height across the annual growing season in this study.</b> Panels (<b>a</b>,<b>b</b>) are the representative varieties in Pattern H-I: two growth periods mainly in spring and summer, especially from June to August with vigorous growth; (<b>c</b>,<b>d</b>) are the representative varieties in Pattern H-II: the three distinct growth periods occurring in March, June, and August. Growth significantly slows during the periods of heavy rainfall and high temperatures. Panels (<b>e</b>,<b>f</b>) are the representative varieties in Pattern H-III: rapid growth in the first half of the year around March to May. Different lines mean the individual trees investigated in each variety.</p>
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<p><b>Primary patterns of growth rhythm in oak ground diameter across the annual growing season in this study.</b> Panels (<b>a</b>,<b>b</b>) are the representative varieties in Pattern D-I: consistent growth throughout the investigated months, notably with rapid growth from summer to autumn; (<b>c</b>,<b>d</b>) are the representative varieties in Pattern D-II: a fluctuating growth throughout the investigated months; (<b>e</b>,<b>f</b>) are the representative varieties in Pattern D-III: two rapid growth periods, respectively, from May to June and August to September. Different lines mean the individual trees investigated in each variety.</p>
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<p><b>Fitted curve of dynamic growth related to oak seedling height and ground diameter.</b> (<b>a</b>–<b>c</b>) Three main patterns of fitted curves for oak seedling height. (<b>d</b>–<b>f</b>) Three main patterns of fitted curves for oak ground diameter. All fitted curves were estimated based on the 200-day investigation.</p>
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<p>Leaf phenotypes of 18 different oak varieties. The bar is 5 cm.</p>
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<p>Leaf morphological investigation and analysis in 18 oak varieties. (<b>a</b>–<b>f</b>) respectively represent Leaf area, Leaf length, Leaf width, Leaf aspect ratio, Leaf form factor and Leaf gap. Different lower-case letters indicate significant differences among different varieties, <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Analysis of photosynthetic parameters for 11 oak candidates. (<b>a</b>) represent chlorophyll content; E: the transpiration rate (<b>b</b>), Ci: intercellular CO<sub>2</sub> concentration (<b>c</b>), Ca: leaf chamber CO<sub>2</sub> concentration (<b>d</b>), gsw: stomatal con-ductance (<b>e</b>), gtw: total vapor conductance (<b>f</b>). Different lowercase letters indicate significant differences among the 11 oak candidates; <span class="html-italic">p</span> &lt; 0.05.</p>
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<p><b>Correlation analysis between different traits investigated from 11 selected oak candidates.</b> Red and blue indicate the positive and negative correlations, respectively. The darker color indicates more significant correlation between the traits (<span class="html-italic">p</span> &lt; 0.05), and the size of the pies represents the correlation coefficient. The lines, respectively, highlight the significant correlation with seedling height and ground diameter, and purple is a positive correlation.</p>
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<p><b>Principal component analysis to identify excellent varieties from 11 selected oak candidates.</b> PC1 and PC2 are principal component 1 and principal component 2; X1–X8 are the loading scores of various investigated traits. Different colored pies show the distribution of 11 oak candidates, which are divided by the red circles.</p>
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26 pages, 19147 KiB  
Article
Ecological Gate Water Control and Its Influence on Surface Water Dynamics and Vegetation Restoration: A Case Study from the Middle Reaches of the Tarim River
by Jie Wu, Fan Gao, Bing He, Fangyu Sheng, Hailiang Xu, Kun Liu and Qin Zhang
Forests 2024, 15(11), 2005; https://doi.org/10.3390/f15112005 - 14 Nov 2024
Viewed by 329
Abstract
Ecological sluices were constructed along the Tarim River to supplement the ecosystem’s water supply. However, the impact of water regulation by these sluices on the surface water area (SWA) and its relationship with the vegetation response remain unclear. To increase the efficiency of [...] Read more.
Ecological sluices were constructed along the Tarim River to supplement the ecosystem’s water supply. However, the impact of water regulation by these sluices on the surface water area (SWA) and its relationship with the vegetation response remain unclear. To increase the efficiency of ecological water use, it is crucial to study the response of SWA to water control by the ecological gates and its relationship with vegetation restoration. We utilized the Google Earth Engine (GEE) cloud platform, which integrates Landsat-5/7/8 satellite imagery and employs methods such as automated waterbody extraction via mixed index rule sets, field investigation data, Sen + MK trend analysis, mutation analysis, and correlation analysis. Through these techniques, the spatiotemporal variations in SWA in the middle reaches of the Tarim River (MROTR) from 1990–2022 were analyzed, along with the relationships between these variations and vegetation restoration. From 1990–2022, the SWA in the MROTR showed an increasing trend, with an average annual growth rate of 12.47 km2 per year. After the implementation of ecological gates water regulations, the SWA significantly increased, with an average annual growth rate of 28.8 km2 per year, while the ineffective overflow within 8 km of the riverbank notably decreased. The NDVI in the MROTR exhibited an upward trend, with a significant increase in vegetation on the northern bank after ecological sluice water regulation. This intervention also mitigated the downward trend of the medium and high vegetation coverage types. The SWA showed a highly significant negative correlation with low-coverage vegetation within a 5-km range of the river channel in the same year and a significant positive correlation with high-coverage vegetation within a 15-km range. The lag effect of SWA influenced the growth of medium- and high-coverage vegetation. These findings demonstrated that the large increase in SWA induced by ecological gate water regulation positively impacted vegetation restoration. This study provides a scientific basis for water resource regulation and vegetation restoration in arid regions globally. Full article
(This article belongs to the Special Issue Application of Remote Sensing in Vegetation Dynamic and Ecology)
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<p>Map of the study area ((<b>a</b>). Elevation maps (<b>b</b>). 2020 Land use type maps).</p>
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<p>Schematic layout of the monitored sample plots in the study area.</p>
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<p>Comparison of waterbody extraction results with JRC data.</p>
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<p>Time series of SWA in the MROTR, 1990–2022.</p>
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<p>Sections S1–S4 SWA in the MROTR, 1990–2022. (<b>a</b>) Coverage of all water bodies,1990-2022. (<b>b</b>) Characteristics of temporal changes in SWA in the S1 region. (<b>c</b>) Characteristics of temporal changes in SWA in the S2 region. (<b>d</b>) S1–S4 regional SWA percentage. (<b>e</b>) Characteristics of temporal changes in SWA in the S3 region. (<b>f</b>) Characteristics of temporal changes in SWA in the S4 region. (<b>g</b>) Comparison of SWA over three time periods.</p>
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<p>Changes in SWA at varying distances from the riverbank in different water volume years. (<b>a</b>) Change in SWA in a normal year. (<b>b</b>) Change in SWA in a wet year. (<b>c</b>) Change in SWA in a wet year. (<b>d</b>) Change in SWA in a extremely wet years year.</p>
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<p>Time series of the interannual vegetation indicators of the MROTR, 2000–2022. (<b>a</b>). Annual mean NDVI (<b>b</b>). June–September monthly mean NDVI (<b>c</b>–<b>f</b>). Annual mean vegetation phenology.</p>
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<p>Spatial distribution and trends of the vegetation cover in the MROTR, 1990–2022.</p>
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<p>Area of each vegetation cover type at different stages before and after ecological gate control.</p>
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<p>Vegetation FVC in the MROTR remote sensing monitoring area in 2016, 2017 and 2018 (each monitoring area corresponds to the vegetation FVC of the year and the surface waterbody of the year).</p>
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<p>Vegetation FVC in the MROTR remote sensing monitoring areas in 2007, 2011, and 2013. Each monitoring area corresponds to the vegetation FVC of the current year and the surface waterbody of the previous year, e.g., Figure 2007a shows the vegetation FVC of 2007 and the surface waterbody of 2006.</p>
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<p>Correlations between water inflows and vegetation cover from 1990 to 2022. (<b>a</b>,<b>b</b>) show the correlations between different water inflows and vegetation cover within 5 km of the riverbank, (<b>c</b>,<b>d</b>) show the correlations between water inflows and vegetation cover within 5 km–15 km from the riverbank. (<b>b</b>,<b>d</b>) show the correlations between water inflows and vegetation cover 1 year after the lag year.</p>
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<p>Correlations between surface water area and annual vegetation characteristics.</p>
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22 pages, 7222 KiB  
Article
Karst Ecosystem: Moso Bamboo Intercropping Enhances Soil Fertility and Microbial Diversity in the Rhizosphere of Giant Lily (Cardiocrinum giganteum)
by Jie Zhang, Haoyu Wu, Guibin Gao, Yuwen Peng, Yilin Ning, Zhiyuan Huang, Zedong Chen, Xiangyang Xu and Zhizhuang Wu
Forests 2024, 15(11), 2004; https://doi.org/10.3390/f15112004 - 13 Nov 2024
Viewed by 273
Abstract
Intercropping affects soil microbial community structure significantly; however, the effects on understory medicinal plants in karst areas remain unclear. We investigated the effects of four intercropping systems (Moso bamboo, Chinese fir, bamboo-fir mixed forest, and forest gap) on the rhizosphere microbial communities of [...] Read more.
Intercropping affects soil microbial community structure significantly; however, the effects on understory medicinal plants in karst areas remain unclear. We investigated the effects of four intercropping systems (Moso bamboo, Chinese fir, bamboo-fir mixed forest, and forest gap) on the rhizosphere microbial communities of giant lily (Cardiocrinum giganteum), an economically important medicinal plant in China. We assessed the intercropping impact on rhizosphere microbial diversity, composition, and co-occurrence networks and identified key soil properties driving the changes. Bacterial and fungal diversity were assessed by 16S rRNA and ITS gene sequencing, respectively; soil physicochemical properties and enzyme activities were measured. Moso bamboo system had the highest fungal diversity, with relatively high bacterial diversity. It promoted a distinct microbial community structure with significant Actinobacteria and saprotrophic fungi enrichment. Soil organic carbon, total nitrogen, and available potassium were the most influential drivers of microbial community structure. Co-occurrence network analysis revealed that the microbial network in the Moso bamboo system was the most complex and highly interconnected, with a higher proportion of positive interactions and a greater number of keystone taxa. Thus, integrating Moso bamboo into intercropping systems can enhance soil fertility, microbial diversity, and ecological interactions in the giant lily rhizosphere in karst forests. Full article
(This article belongs to the Special Issue Ecological Research in Bamboo Forests)
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<p>Soil physicochemical properties in the giant lily rhizosphere under different intercropping systems: (<b>a</b>) total organic carbon (TOC), (<b>b</b>) total nitrogen (TN), (<b>c</b>) total phosphorus (TP), (<b>d</b>) available nitrogen (AN), (<b>e</b>) available phosphorus (AP), (<b>f</b>) available potassium (AK), (<b>g</b>) pH, (<b>h</b>) β-D-glucosidase (BDG), (<b>i</b>) acid phosphatase (ACP), (<b>j</b>) N-acetyl-β-D-glucosaminidase (NAG), and (<b>k</b>) leucine aminopeptidase (LAP). Error bars represent standard deviations (n = 5). Different lowercase letters indicate significant differences among systems (LSD post hoc test, <span class="html-italic">p</span> ≤ 0.05).</p>
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<p>Amplicon Sequence Variant (ASV) richness of (<b>a</b>) bacteria and (<b>b</b>) fungi in the giant lily rhizosphere under different intercropping systems; blue circles indicate shared taxa across systems; grey circles indicate non-shared ASVs; black bars indicate the number of shared taxa.</p>
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<p>Alpha diversity indices of (<b>a</b>–<b>c</b>) bacterial and (<b>d</b>–<b>f</b>) fungal communities in the giant lily rhizosphere under different intercropping systems. Lowercase letters indicate significant differences among systems (<span class="html-italic">p</span> = 0.05).</p>
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<p>Principal coordinate analysis (PCoA) and analysis of similarities (ANOSIM) tests of (<b>a</b>,<b>b</b>) bacterial and (<b>c</b>,<b>d</b>) fungal communities in the giant lily rhizosphere under different intercropping systems.</p>
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<p>Composition and linear discriminant analysis effect size (LEfSe) analysis of bacterial and fungal communities in the giant lily rhizosphere under different intercropping systems. (<b>a</b>,<b>b</b>) Relative abundance at the phylum level; (<b>c</b>,<b>d</b>) LEfSe results (phylum to genus level).</p>
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<p>Redundancy analysis (RDA) of (<b>a</b>) bacterial and (<b>b</b>) fungal communities in the giant lily rhizosphere under different intercropping systems.</p>
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<p>Functional predictions and correlations with dominant phyla for (<b>a</b>) bacterial functional annotation of prokaryotic taxa (FAPROTAX) and (<b>b</b>) fungal functional guilds (FUNGuild) in the giant lily rhizosphere under different intercropping systems. (<b>c</b>) Correlation analysis between dominant functional groups and dominant bacterial phyla. Asterisks indicate significance levels: * (0.01&lt; <span class="html-italic">p</span> ≤ 0.05), ** (0.001&lt; <span class="html-italic">p</span> ≤ 0.01).</p>
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<p>Co-occurrence networks of bacterial and fungal communities in the giant lily rhizosphere under different intercropping systems: (<b>a</b>,<b>e</b>) bamboo–giant lily, (<b>b</b>,<b>f</b>) Chinese fir–giant lily, (<b>c</b>,<b>g</b>) Moso bamboo–giant lily, and (<b>d</b>,<b>h</b>) forest gap–giant lily intercropping.</p>
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<p>Co-occurrence networks of bacterial and fungal communities in the giant lily rhizosphere under different intercropping systems: (<b>a</b>,<b>e</b>) bamboo–giant lily, (<b>b</b>,<b>f</b>) Chinese fir–giant lily, (<b>c</b>,<b>g</b>) Moso bamboo–giant lily, and (<b>d</b>,<b>h</b>) forest gap–giant lily intercropping.</p>
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21 pages, 2608 KiB  
Article
An Interval Fuzzy Programming Approach to Solve a Green Intermodal Routing Problem for Timber Transportation Under Uncertain Information
by Yan Sun, Chen Zhang and Guohua Sun
Forests 2024, 15(11), 2003; https://doi.org/10.3390/f15112003 - 13 Nov 2024
Viewed by 261
Abstract
This study investigates an intermodal routing problem for transporting wood from a storage yard of the timber harvest area to a timber mill, in which the transfer nodes in the intermodal transportation network have multiple service time windows. To improve the environmental sustainability [...] Read more.
This study investigates an intermodal routing problem for transporting wood from a storage yard of the timber harvest area to a timber mill, in which the transfer nodes in the intermodal transportation network have multiple service time windows. To improve the environmental sustainability of timber transportation, a carbon tax policy is employed in the routing to reduce the carbon emissions. Uncertain information on the capacities and carbon emission factors of the transportation activities in the intermodal transportation network is modeled using interval fuzzy numbers to enhance the feasibility of the routing optimization in the actual timber transportation. Based on the above consideration, an interval fuzzy nonlinear optimization model is established to handle the specific routing problem. Model defuzzification and linearization are then conducted to obtain an equivalent formulation that is crisp and linear to make the global optimum solution attainable. A numerical experiment is conducted to verify the feasibility of the proposed model, and it reveals the influence of the optimization level and service time windows on the routing optimization, and it confirms that intermodal transportation is suitable for timber transportation. This experiment also analyzes the feasibility of a carbon tax policy in reducing the carbon emissions of timber transportation, and it finds that the performance of this policy is determined by the optimization level given by the timber mill and is not always feasible in all cases. For the case where a carbon tax policy is infeasible, this study proposes a bi-objective optimization that can use Pareto solutions to balance the economic and environmental objectives as an alternative. The bi-objective optimization further shows the relationship between lowering the transportation costs, reducing the carbon emissions, and enhancing the reliability on capacity and budget by improving the optimization level. The conclusions provide managerial insights that can help the timber mill and intermodal transportation operator organize cost-efficient, low-carbon, and reliable intermodal transportation for timber distribution, and support sustainable forest logistics. Full article
(This article belongs to the Special Issue Optimization of Forestry and Forest Supply Chain)
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<p>Diagram of intermodal routing for timber transportation.</p>
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<p>Structure of intermodal transportation network in the numerical experiment [<a href="#B41-forests-15-02003" class="html-bibr">41</a>].</p>
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<p>Sensitivity of the intermodal routing optimization for timber transportation concerning the optimization level.</p>
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<p>Total costs of intermodal routing and road-based unimodal routing for timber transportation.</p>
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<p>Carbon emissions of intermodal routing and road-based unimodal routing for timber transportation.</p>
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<p>Total costs of intermodal routing with and without service time windows for timber transportation.</p>
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<p>Carbon emissions of intermodal routing with and without service time windows for timber transportation.</p>
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<p>Carbon emissions of intermodal routing under the carbon tax policy and carbon emission minimization for timber transportation.</p>
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<p>Distributions of <math display="inline"><semantics> <mrow> <mi mathvariant="normal">P</mi> <mi mathvariant="normal">o</mi> <mi mathvariant="normal">s</mi> <mi mathvariant="normal">s</mi> <mfenced open="{" close="}" separators="|"> <mrow> <mover accent="true"> <mrow> <mi>a</mi> </mrow> <mo>~</mo> </mover> <mo>≥</mo> <mi>b</mi> </mrow> </mfenced> </mrow> </semantics></math> and <math display="inline"><semantics> <mrow> <mi mathvariant="normal">P</mi> <mi mathvariant="normal">o</mi> <mi mathvariant="normal">s</mi> <mi mathvariant="normal">s</mi> <mfenced open="{" close="}" separators="|"> <mrow> <mover accent="true"> <mrow> <mi>a</mi> </mrow> <mo>~</mo> </mover> <mo>≤</mo> <mi>b</mi> </mrow> </mfenced> </mrow> </semantics></math>.</p>
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22 pages, 16916 KiB  
Article
Estimation of Understory Fine Dead Fuel Moisture Content in Subtropical Forests of Southern China Based on Landsat Images
by Zhengjie Li, Zhiwei Wu, Shihao Zhu, Xiang Hou and Shun Li
Forests 2024, 15(11), 2002; https://doi.org/10.3390/f15112002 - 13 Nov 2024
Viewed by 239
Abstract
The understory fine dead fuel moisture content (DFMC) is an important reference indicator for regional forest fire warnings and risk assessments, and determining it on a large scale is a critical goal. It is difficult to estimate understory fine DFMC directly from satellite [...] Read more.
The understory fine dead fuel moisture content (DFMC) is an important reference indicator for regional forest fire warnings and risk assessments, and determining it on a large scale is a critical goal. It is difficult to estimate understory fine DFMC directly from satellite images due to canopy shading. To address this issue, we used canopy meteorology estimated by Landsat images in combination with explanatory variables to construct random forest models of in-forest meteorology, and then construct random forest models by combining the meteorological factors and explanatory variables with understory fine DFMC obtained from the monitoring device to (1) investigate the feasibility of Landsat images for estimating in-forest meteorology; (2) explore the feasibility of canopy or in-forest meteorology and explanatory variables for estimating understory fine DFMC; and (3) compare the effects of each factor on model accuracy and its effect on understory fine DFMC. The results showed that random forest models improved in-forest meteorology estimation, enhancing in-forest relative humidity, vapor pressure deficit, and temperature by 50%, 34%, and 2.2%, respectively, after adding a topography factor. For estimating understory fine DFMC, models using vapor pressure deficit improved fit by 10.2% over those using relative humidity. Using in-forest meteorology improved fits by 36.2% compared to canopy meteorology. Including topographic factors improved the average fit of understory fine DFMC models by 123.1%. The most accurate model utilized in-forest vapor pressure deficit, temperature, topographic factors, vegetation index, precipitation data, and seasonal factors. Correlations indicated that slope, in-forest vapor pressure deficit, and slope direction were most closely related to understory fine DFMC. The regional understory fine-grained DFMC distribution mapped according to our method can provide important decision support for forest fire risk early warning and fire management. Full article
(This article belongs to the Special Issue Forest Disturbance and Management)
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<p>Study area.</p>
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<p>Technical route map. Explanatory variables: topography, precipitation data, vegetation index, season; R-F: Random Forest. The “+” symbol serves a connecting function.</p>
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<p>Understory fine DFMC monitoring device. Sample bags were predominantly filled with fuels from the ground and were weighed when the bags were pulled up to minimize interference from ground vegetation that could affect the weighing.</p>
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<p>Visualization of the fitted models for in-forest meteorological assessment. The black solid line represents the 1:1 line, the black dashed line represents the fitted line, and the gray shaded area indicates the 95% confidence interval. The <span class="html-italic">y</span>-axis displays the predicted values, and the <span class="html-italic">x</span>-axis displays the observed values. Red dots indicate low predicted values, while blue dots indicate high predicted values. (<b>a</b>–<b>c</b>) The fitting results of the models that consider topography: forest interior relative humidity (IFRH-scheme1), vapor pressure deficit (IFD-scheme1), and temperature (IFT-scheme1). (<b>d</b>–<b>f</b>) The fitting results of the models that do not consider topography: forest interior relative humidity (IFRH-scheme2), vapor pressure deficit (IFD-scheme2), and temperature (IFT-scheme2). The meanings of the abbreviations for each scheme are provided in <a href="#forests-15-02002-t001" class="html-table">Table 1</a> and <a href="#forests-15-02002-t003" class="html-table">Table 3</a>.</p>
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<p>Visualization of the fitted models for understory fine DFMC. The black solid line represents the 1:1 line, the black dashed line represents the fitted line, and the gray shaded area indicates the 95% confidence interval. The <span class="html-italic">y</span>-axis displays the predicted values, and the <span class="html-italic">x</span>-axis displays the observed values. Red dots indicate lower predicted values, while blue dots indicate higher predicted values. (<b>a</b>–<b>d</b>) The fitting results of the understory fine DFMC models using relative humidity. (<b>e</b>–<b>h</b>) The fitting results of the understory fine DFMC models using vapor pressure deficit. Among these, (<b>a</b>,<b>b</b>,<b>e</b>,<b>f</b>) incorporate topography in the modeling, while (<b>b</b>,<b>d</b>,<b>f</b>,<b>h</b>) use in-forests meteorology in the modeling. The detailed information on each model and the abbreviations for schemes are provided in <a href="#forests-15-02002-t003" class="html-table">Table 3</a>.</p>
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<p>Visualization of the contributions of factors to in-forest meteorological modeling. (<b>a</b>) The factor contribution rates for the in-forest vapor pressure deficit model. (<b>b</b>) The factor contribution rates for the in-forest humidity model. (<b>c</b>) The factor contribution rates for the in-forest temperature model. Values are percent contribution, with the minimum value set to 0. The meanings of the abbreviations of factors are provided in <a href="#forests-15-02002-t001" class="html-table">Table 1</a>.</p>
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<p>Visualization of the contributions of factors and their correlations in D-DFMC-scheme2. (<b>a</b>) The contribution of the factors to the model, (<b>b</b>) the correlation and significance of each factor with the understory fine DFMC. The meanings of the abbreviations of factors are provided in <a href="#forests-15-02002-t001" class="html-table">Table 1</a>.</p>
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<p>Relationships between understory fine DFMC and various factors (In-forest meteorology: (<b>a</b>,<b>b</b>); <span class="html-italic">NDVI</span>: (<b>c</b>); Season: (<b>d</b>); Precipitation data: (<b>e</b>,<b>f</b>); Topography: (<b>g</b>–<b>i</b>)). Black lines indicate fitted curves. Darker colors represent higher moisture content. The abbreviations used for the <span class="html-italic">x</span>-axis labels in each subplot are provided in <a href="#forests-15-02002-t001" class="html-table">Table 1</a>.</p>
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<p>Visualization of estimated in-forest temperature and vapor pressure deficit. Cloud-free remote sensed images were selected from each season for mapping. (<b>a</b>,<b>b</b>) The in-forest temperature and vapor pressure deficit for the four seasons in Nankang and Yudu, respectively. White areas represent regions without vegetation cover, and the acquisition times of the images are indicated above each figure.</p>
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<p>Visualization of estimated understory fine DFMC. Cloud-free remote sensed images were selected from each season for mapping. Understory fine DFMC maps for Nankang and Yudu were generated for the four seasons. White areas represent regions without vegetation cover, and the acquisition times of the images are indicated above each figure.</p>
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<p>Examples of fine dead fuel samples. (<b>a</b>) Sample of <span class="html-italic">pinus</span>. (<b>b</b>) Sample of <span class="html-italic">Cunninghamia lanceolata</span>. (<b>c</b>) Sample of <span class="html-italic">Liquidambar formosana Hance</span>. (<b>d</b>) Sample of <span class="html-italic">Schima superba</span>.</p>
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14 pages, 6498 KiB  
Article
Qualitative Wood Anatomy Study of Ottobratica and Sinopolese Cultivars of Olea europaea L.
by Tiziana Urso, Michela Zanetti, Annalisa Magnabosco, Angelo Mammoliti, Marco Paccagnella and Andrea Rosario Proto
Forests 2024, 15(11), 2001; https://doi.org/10.3390/f15112001 - 13 Nov 2024
Viewed by 331
Abstract
Olive wood is used in a niche economic context but is attracting growing interest. In this study, the wood anatomy of Olea europaea L. belonging to two cultivars cultivated in the Plain of Gioia Tauro in Calabria (RC) is qualitatively described. Wood samples [...] Read more.
Olive wood is used in a niche economic context but is attracting growing interest. In this study, the wood anatomy of Olea europaea L. belonging to two cultivars cultivated in the Plain of Gioia Tauro in Calabria (RC) is qualitatively described. Wood samples were obtained along the diameter of wood slices to investigate any anatomical differences between the inner and outer zones of the stem. The microscopic slides were investigated using an optical microscope. The anatomical characteristics observed were compared with existing literature data. The two cultivars show parenchyma rays arranged not only in one to two rows (typical of this species), but also in three rows. Furthermore, in both cultivars, the presence of starch deposits in procumbent parenchyma cells was observed. The Ottobratica cultivar seems to have more starch than the Sinopolese one, but given the high variability of olive wood, further quantitative analysis is needed to determine whether these differences are statistically valid and due to the different cultivars. This work can contribute to a better understanding of the Olea europaea L. species and to a better technical valorisation of its wood. Full article
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<p>Olive trees (<span class="html-italic">Olea europaea</span> L.) examined in this study.</p>
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<p>Olive wood (<span class="html-italic">Olea europaea</span> L.) slices: (<b>A</b>) Sinopolese cultivar wood and (<b>B</b>) Ottobratica cultivar wood.</p>
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<p>Olive wood cultivar samples: Sinopolese (<b>a</b>) and Ottobratica (<b>b</b>). Small red squares indicate where the samples were cut with the respective codes (sample 0 is the pith).</p>
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<p>Olive heartwood cross-section: (<b>A</b>) Sinopolese cultivar: sample 1B; (<b>B</b>) Ottobratica cultivar: sample 2A. Diffuse–porous wood (IAWA feature 5). Vessels in radial/diagonal pattern (IAWA feature 7). Vessels partly solitary, partly in radial multiples of 2–4, or in very small clusters (IAWA features 10, 11). Parenchyma scantly paratracheal/vasicentric (IAWA features 78,79). Presence of common tylosis (IAWA features 56), gums, and other deposits (IAWA feature 58) [<a href="#B26-forests-15-02001" class="html-bibr">26</a>].</p>
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<p>Sinopolese olive wood cultivar: (<b>A</b>) 15B sample, sapwood. Radial section, red arrow: simple perforations plate (IAWA feature 13); (<b>B</b>) 12B sample, heartwood. Tangential section, red arrow: alternate inter-vessel pits (IAWA feature 22) [<a href="#B26-forests-15-02001" class="html-bibr">26</a>].</p>
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<p>Ottobratica olive wood cultivar: 5A sample, sapwood, tangential section. Red circles: helical thickenings only in vessel element tails (IAWA features 36 and 38 [<a href="#B26-forests-15-02001" class="html-bibr">26</a>]).</p>
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<p>Olive wood. (<b>A</b>) Ottobratica cultivar, 4B sample. (<b>B</b>) Sinopolese cultivar, 1B sample. Heartwood, tangential section. Presence of common tylosis (red arrows, IAWA features 56), gums and other deposits (IAWA feature 58) [<a href="#B26-forests-15-02001" class="html-bibr">26</a>].</p>
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<p>Sinopolese olive wood cultivar: (<b>A</b>) 1B sample, heartwood; (<b>B</b>) 15B sample, sapwood. Tangential section. Yellow boxes: ray width with one to three cells (IAWA feature 97 [<a href="#B26-forests-15-02001" class="html-bibr">26</a>]).</p>
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<p>Olive wood, heartwood radial sections. (<b>A</b>) Sinopolese, 1B sample; (<b>B</b>) Ottobratica, 4B sample. Red arrow: body ray cells procumbent with mostly two to four upright rows (IAWA feature 107). Red arrow: rays with procumbent, square, and upright cells mixed throughout the ray (IAWA feature 109) [<a href="#B26-forests-15-02001" class="html-bibr">26</a>].</p>
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<p>Starch (black spots) in Ottobratica olive wood cultivar, 5A sample, sapwood. (<b>A</b>) Radial section, (<b>B</b>) tangential section.</p>
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<p>Starch (black spots) in Sinopolese olive wood cultivar, 15B sample, sapwood (radial section).</p>
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14 pages, 2686 KiB  
Article
Analysis of the Diversity of Corticolous Lichens Associated with Tree Trunks in the Understories of Four Tropical Dry Forests of the Atlántico Department in Colombia
by Pierine España-Puccini, Juan P. Gómez, Amner Muñoz-Acevedo, Daniel Posada-Echeverría and María C. Martínez-Habibe
Forests 2024, 15(11), 2000; https://doi.org/10.3390/f15112000 - 13 Nov 2024
Viewed by 305
Abstract
Tropical dry forests (TDFs) are unique ecosystems with high biodiversity, including a rich variety of lichen species. Lichens are sensitive to environmental changes and can serve as bioindicators of ecosystem health. This study examined the diversity of lichen communities at four TDF sites [...] Read more.
Tropical dry forests (TDFs) are unique ecosystems with high biodiversity, including a rich variety of lichen species. Lichens are sensitive to environmental changes and can serve as bioindicators of ecosystem health. This study examined the diversity of lichen communities at four TDF sites in the Atlántico Department of Colombia. More than 700 tree lichen specimens were collected and identified at the four sites. A total of 135 species of lichens were identified, of which 19 are possibly undescribed. The most diverse sites were Usiacurí and Repelón, both protected areas with relatively well-preserved forests. The findings of this study demonstrate that the Atlántico TDFs host a large diversity of lichens, with a significant number of records of new species. The observed differences in species composition between sites highlight the importance of habitat heterogeneity and anthropogenic pressures on lichen communities. The results emphasize the need for conservation strategies to protect these ecologically valuable lichen communities within the Atlántico TDFs. Full article
(This article belongs to the Special Issue Forest Biodiversity Conservation)
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<p>Locations of the four sampling sites of the Department of Atlántico where lichens were collected.</p>
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<p>Lichen taxa in the Department of Atlántico. Each sampling site is represented by a different color, while the size of the circle is related to the number of species in each genus.</p>
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<p>Lichen taxa accumulation curves for four sites at the Department of Atlántico (<b>A</b>) for each sampling site: (<b>B</b>) Tubará, (<b>C</b>) Piojó, (<b>D</b>) Repelón and (<b>E</b>) Usiacurí. The grey polygons show the 95% confidence intervals of the accumulation curves.</p>
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<p>Community diversity indices observed and estimated for the Department of Atlántico (γ-diversity) and for each sampling site (α-diversity). (<b>A</b>) q0, (<b>B</b>) q1 and (<b>C</b>) q2.</p>
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<p>Lichen community between sampling sites in the Department of Atlántico. (<b>A</b>) Non-metric multidimensional scaling based on the Bray-Curtis dissimilarity matrix generated with the information of all sampled trees. Each point represents a tree in a sampling site (colors) and the distance between points is proportional to the value of the Bray-Curtis dissimilarity index between two trees. (<b>B</b>) Values of the different components of community dissimilarity, namely nesting and turnover, for each pair of sampling sites. In this case, each point represents a comparison between the sampling sites.</p>
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21 pages, 5113 KiB  
Article
A 35-Year Analysis of Vegetation Cover in Rare-Earth Mining Areas Using Landsat Data
by Zhubin Zheng, Yuqing Liu, Na Chen, Ge Liu, Shaohua Lei, Jie Xu, Jianzhong Li, Jingli Ren and Chao Huang
Forests 2024, 15(11), 1999; https://doi.org/10.3390/f15111999 - 13 Nov 2024
Viewed by 227
Abstract
Fractional vegetation cover (FVC) plays a significant role in assessing ecological quality and protection, as well as soil and water conservation. As a typical rare-earth resource county in China, Dingnan County has experienced rapid development due to rare-earth mining, resulting in significant alterations [...] Read more.
Fractional vegetation cover (FVC) plays a significant role in assessing ecological quality and protection, as well as soil and water conservation. As a typical rare-earth resource county in China, Dingnan County has experienced rapid development due to rare-earth mining, resulting in significant alterations to vegetation cover. To elucidate the spatio-temporal changes in vegetation within Dingnan County over the past 35 years and the effects of natural and human factors on these changes, the spatial and temporal variations in FVC were analyzed using Landsat-TM/OLI multispectral images taken in 1988, 1995, 1997, 2002, 2006, 2013, 2017, and 2023. The findings indicate that (1) vegetation coverage in Dingnan County decreased from 1988 to 2002, followed by a gradual increase; (2) high vegetation cover is predominantly found in forested areas that maintain their natural state, while the central town and mining areas exhibit generally low coverage; (3) there are regional differences in the relationship between vegetation cover and environmental factors in Dingnan County. This research facilitates the alignment of ion-type rare-earth mining with ecological protection, thereby promoting the sustainable development of the mining area and providing scientific guidance for local governments to formulate more effective management and protection strategies for the mining ecosystem. Additionally, this research offers a scientific foundation for mining areas globally to develop sustainable policies and informed decision-making regarding environmental protection and sustainable development. Full article
(This article belongs to the Section Forest Ecology and Management)
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<p>Study area. (<b>a</b>) The location of Jiangxi Province; (<b>b</b>) the location of the study area in Jiangxi Province; (<b>c</b>) the Lingbei rare-earth mining area in Dingnan County. Orange star is the location of Lingbei rare-earth mining area.</p>
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<p>Specific research process.</p>
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<p>(<b>a</b>) The mean change in FVC from 1988 to 2023, and the blue line is a linear fitting line. (<b>b</b>) Corresponding area (km<sup>2</sup>) of vegetation cover grade in Dingnan County, 1988–2023.</p>
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<p>(<b>a</b>–<b>d</b>) Reclassification map of vegetation coverage in Dingnan County, 1988–2002. (<b>e</b>) Vegetation coverage statistics of Dingnan County, 1988–2002.</p>
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<p>(<b>a</b>–<b>c</b>) Vegetation cover reclassification map of Dingnan County, 2002–2013. (<b>d</b>) Vegetation coverage statistics of Dingnan County from 2002 to 2013.</p>
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<p>(<b>a</b>–<b>c</b>) Vegetation cover reclassification map of Dingnan County, 2013–2023. (<b>d</b>–<b>f</b>) Vegetation coverage statistics of Dingnan County from 2013 to 2023.</p>
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<p>Results of the interaction of influencing factors on FVC in Dingnan County (X1 represents surface temperature, X2 represents average annual precipitation, X3 represents average temperature, X4 represents average wind speed, X5 represents night light value, X6 represents GDP, X7 represents population, and X8 represents soil erosion).</p>
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<p>Results of the interaction of influencing factors on FVC in Lingbei mining area (X1 represents surface temperature, X2 represents average annual precipitation, X3 represents average temperature, X4 represents average wind speed, X5 represents night light value, X6 represents GDP, X7 represents population, and X8 represents soil erosion).</p>
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<p>(<b>a</b>) Schedule of events affecting FVC change in Dingnan County. (<b>b</b>) The area change in relatively low-grade vegetation coverage in Dingnan County and Lingbei mining area.</p>
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23 pages, 1558 KiB  
Article
Empowering Forestry Management and Farmers’ Income Growth Through the Digital Economy—Empirical Evidence from Guizhou Province, China
by Lei Yao, Li Ma, Kaiwen Su, Mengxuan Wang, Wei Duan and Yali Wen
Forests 2024, 15(11), 1998; https://doi.org/10.3390/f15111998 - 13 Nov 2024
Viewed by 253
Abstract
Facilitating the sustained and stable growth of farmers’ income is crucial for achieving sustainable development in forest regions. As an emerging driving force, the digital economy has demonstrated substantial potential in enhancing farmers’ income and promoting regional economic prosperity in forest areas. Based [...] Read more.
Facilitating the sustained and stable growth of farmers’ income is crucial for achieving sustainable development in forest regions. As an emerging driving force, the digital economy has demonstrated substantial potential in enhancing farmers’ income and promoting regional economic prosperity in forest areas. Based on survey data from 1043 households across 10 counties in Guizhou Province, China, this study empirically examined the direct and indirect effects of digital economy participation on income growth among farmers in forest regions. The findings revealed that, first, participation in the digital economy significantly contributed to income growth for these households. This effect remained robust across various estimation methods, restricted sample tests, and when replacing dependent variables. Second, forestry management and its diversification played a mediating role in the relationship between digital economy participation and farmers’ income. Participation in the digital economy indirectly influenced income growth by fostering forestry management activities and their diversification. Third, the heterogeneity analysis indicated that digital economy participation had a significant positive impact on the income growth of pure farming households, part-time farming households, and households that had previously escaped poverty. This discovery underscored the unique role of the digital economy in alleviating poverty and preventing its recurrence. The conclusions of this study provide essential theoretical and practical guidance for empowering forestry development through the digital economy and advancing the digital transformation of the forestry industry. More critically, this research presents a novel pathway for the deep integration of the digital economy with forestry, jointly fostering income growth for farmers in forest regions, which holds significant implications for achieving rural sustainable development. Full article
(This article belongs to the Section Forest Economics, Policy, and Social Science)
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<p>Research area.</p>
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<p>Kernel density distribution of treatment and control groups before and after matching.</p>
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13 pages, 2514 KiB  
Article
Light Drought Stress Positively Influenced Root Morphological and Endogenous Hormones in Pinus massoniana Seedlings Inoculated with Suillus luteus
by Yi Wang, Youzhi Ren, Guiying Tu, Xuemei Luo and Zhiyuan Zhang
Forests 2024, 15(11), 1997; https://doi.org/10.3390/f15111997 - 13 Nov 2024
Viewed by 334
Abstract
Aims An ectomycorrhizal fungus (ECMF) may enhance plant drought resistance. However, there is limited information regarding the effects of ECMFs on drought resistance in Pinus massoniana Lamb., a native species representing an afforestation pioneer tree in subtropical regions of China. Methods In this [...] Read more.
Aims An ectomycorrhizal fungus (ECMF) may enhance plant drought resistance. However, there is limited information regarding the effects of ECMFs on drought resistance in Pinus massoniana Lamb., a native species representing an afforestation pioneer tree in subtropical regions of China. Methods In this study, a pot experiment was conducted to determine the effects of ECMF Suillus luteus inoculation on the root morphology and endogenous hormones of P. massoniana, including roots, leaves, and stems, under various water treatment conditions. Four water levels (regular, light, moderate, and severe drought) and three inoculations (inoculated Suillus luteus, numbered S12 and S13, and non-ECMF-inoculated) were compared using a factorial design. Results Under drought stress, P. massoniana seedlings inoculated with S12 and S13 had significantly increased root morphology development (p < 0.05). Light drought positively influenced root development, resulting in a more than twofold increase in root length and root surface area compared to non-inoculated seedlings. Concentrations of gibberellic acid (GA), zeatin riboside (ZR), and indole-3-acetic acid (IAA) in roots, stems, and leaves of inoculated S12 and S13 plants were elevated, whereas abscisic acid (ABA) concentrations were significantly lower, compared to non-inoculated seedlings. The ABA concentrations in the roots of S12 and S13 inoculated seedlings under light drought stress were 1.5 times lower than those in non-inoculated controls. Moreover, root development was positively correlated with plant total GA, IAA, and ZR but negatively correlated with ABA. ConclusionsS. luteus can promote the root growth and development of P. massoniana seedlings, notably by regulating the balance in the concentration of endogenous hormones, thus improving the drought resistance of P. massoniana seedlings. Full article
(This article belongs to the Special Issue Topicalities in Forest Ecology of Seeds, 2nd Edition)
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<p>Effect of <span class="html-italic">Suillus luteus</span> on root morphology, assessed as (<b>a</b>) total root length, (<b>b</b>) projection area, (<b>c</b>) total root surface area, (<b>d</b>) total root volume, (<b>e</b>) root tip number, (<b>f</b>) connection count, (<b>g</b>) average number of first-order lateral roots, and (<b>h</b>) angle of first-order lateral root of <span class="html-italic">Pinus massoniana</span> seedlings under drought stress. CK, non-ECMF-inoculated; ND, no drought stress; LD, light drought stress; MD, moderate drought stress; SD, severe drought stress; DS, drought stress. Different lowercase letters above the bars indicate significant differences between the treatments under the same drought stress condition (Duncan test at <span class="html-italic">p</span> &lt; 0.05). Data are mean ± SE of three replicates (<span class="html-italic">n</span> = 3). Two-way ANOVA output: ns, not significant; ** <span class="html-italic">p</span> &lt; 0.01.</p>
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<p>Effects of <span class="html-italic">Suillus luteus</span> on gibberellic acid concentration in roots (<b>a</b>), stems (<b>b</b>), and leaves (<b>c</b>) of <span class="html-italic">Pinus massoniana</span> seedlings under drought stress. NM, non-ECMF-inoculated; ND, no drought stress; LD, light drought; MD, moderate drought; SD, severe drought; DS, drought stress. Different lowercase letters above the bars indicate significant differences between the treatments under the same drought stress condition (Duncan test at <span class="html-italic">p</span> &lt; 0.05). Data are mean ± SE of three replicates (n = 3). Two-way ANOVA output: ns, not significant; ** <span class="html-italic">p</span> &lt; 0.01.</p>
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<p>Effects of <span class="html-italic">Suillus luteus</span> on zeatin riboside concentration in roots (<b>a</b>), stems (<b>b</b>), and leaves (<b>c</b>) of <span class="html-italic">Pinus massoniana</span> seedlings under drought stress. NM, non-ECMF-inoculated; ND, no drought stress; LD, light drought; MD, moderate drought; SD, severe drought; DS, drought stress. Different lowercase letters above the bars indicate significant differences between the treatments under the same drought stress condition (Duncan test at <span class="html-italic">p</span> &lt; 0.05). Data are mean ± SE of three replicates (<span class="html-italic">n</span> = 3). Two-way ANOVA output: ns, not significant; ** <span class="html-italic">p</span> &lt; 0.01.</p>
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<p>Effects of <span class="html-italic">Suillus luteus</span> on indole-3-acetic acid concentration in roots (<b>a</b>), stems (<b>b</b>), and leaves (<b>c</b>) of <span class="html-italic">Pinus massoniana</span> seedlings under drought stress. NM, non-ECMF-inoculated; ND, no drought stress; LD, light drought; MD, moderate drought; SD, severe drought; DS, drought stress. Different lowercase letters above the bars indicate significant differences among the treatments under the same drought stress condition (Duncan test at <span class="html-italic">p</span> &lt; 0.05). Data are mean ± SE of three replicates (<span class="html-italic">n</span> = 3). Two-way ANOVA output: ns, not significant; ** <span class="html-italic">p</span> &lt; 0.01.</p>
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<p>Effects of <span class="html-italic">Suillus luteus</span> on abscisic acid concentration in roots (<b>a</b>), stems (<b>b</b>), and leaves (<b>c</b>) of <span class="html-italic">Pinus massoniana</span> seedlings under drought stress. NM, non-ECMF-inoculated; ND, no drought stress; LD, light drought; MD, moderate drought; SD, severe drought; DS, drought stress. Different lowercase letters above the bars indicate significant differences between the treatments under the same drought stress condition (Duncan test at <span class="html-italic">p</span> &lt; 0.05). Data are mean ± SE of three replicates (<span class="html-italic">n</span> = 3), two-way ANOVA output: ns, not significant; * <span class="html-italic">p</span> &lt; 0.05; ** <span class="html-italic">p</span> &lt; 0.01.</p>
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<p>Pearson correlation coefficients between root morphology and endogenous hormone levels in mycorrhizal colonization of <span class="html-italic">Pinus massoniana</span> seedlings under drought stress (n = 36). (<b>a</b>) Correlation heat map; (<b>b</b>) key index correlation matrix. Note: GA, gibberellic acid; ZR, zeatin riboside; IAA, indole-3-acetic acid; ABA, abscisic acid. *** <span class="html-italic">p</span> &lt; 0.001, ** <span class="html-italic">p</span> &lt; 0.01, * <span class="html-italic">p</span> &lt; 0.05.</p>
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11 pages, 1096 KiB  
Article
Spatiotemporal Dynamics of Trunk-Injected Pesticide Residue for Management of Pine Wilt Disease in Pinus koraiensis
by Min-Jung Kim, Junheon Kim, Nam Sik Yoo and Jong-Kook Jung
Forests 2024, 15(11), 1996; https://doi.org/10.3390/f15111996 - 12 Nov 2024
Viewed by 310
Abstract
This study focused on the persistence, distribution, and efficacy of trunk-injected pesticides in Pinus koraiensis (Korean pine) with regard to controlling pinewood nematodes (PWNs, Bursaphelenchus xylophilus), the causative agent of pine wilt disease (PWD). In this study, we compared pesticide residues in [...] Read more.
This study focused on the persistence, distribution, and efficacy of trunk-injected pesticides in Pinus koraiensis (Korean pine) with regard to controlling pinewood nematodes (PWNs, Bursaphelenchus xylophilus), the causative agent of pine wilt disease (PWD). In this study, we compared pesticide residues in the needles and branches of Korean pine, revealing significant declines in pesticide residues over time after treatments were applied. Notably, abamectin residues decreased from 0.2325 mg/kg to 0.0901 mg/kg in branches over a period of 18 months. In contrast, emamectin benzoate showed a variation in residue decline depending on the formulation, with the residue level in branches decreasing from 0.1220 mg/kg to 0.0328 mg/kg over the same period. From a spatial perspective, the results revealed minimal differences in pesticide residue at varying tree heights, although a decrease in upper canopy residue was observed in some cases. The nematicidal efficacy test demonstrated that none of the treated trees developed PWN symptoms. Overall, the findings suggest that the trunk-injected pesticides abamectin and emamectin benzoate can persist for two years, with the residue levels being sufficient to prevent PWN propagation, even when the levels are below critical inhibition concentrations. Full article
(This article belongs to the Section Forest Ecology and Management)
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Graphical abstract

Graphical abstract
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<p>Temporal variation in pesticide residue in branches and needles (see variable time in <a href="#forests-15-01996-t003" class="html-table">Table 3</a> for statistical results). The values were transformed with a square root.</p>
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20 pages, 6877 KiB  
Article
Improved Prototypical Network Model for Classification of Farmland Shelterbelt Using Sentinel-2 Imagery
by Yueting Wang, Qiangzi Li, Hongyan Wang, Yuan Zhang, Xin Du, Yunqi Shen and Yong Dong
Forests 2024, 15(11), 1995; https://doi.org/10.3390/f15111995 - 12 Nov 2024
Viewed by 357
Abstract
Farmland shelterbelt plays an important role in protecting farmland and ensuring stable crop yields, and it is mainly distributed in the form of bands and patches; different forms of distribution have different impacts on farmland, which is an important factor affecting crop yields. [...] Read more.
Farmland shelterbelt plays an important role in protecting farmland and ensuring stable crop yields, and it is mainly distributed in the form of bands and patches; different forms of distribution have different impacts on farmland, which is an important factor affecting crop yields. Therefore, high-precision classification of banded and patch farmland shelterbelt is a prerequisite for analyzing its impact on crop yield. In this study, we explored the effectiveness and transferability of an improved Prototypical Network model incorporating data augmentation and a convolutional block attention module for extracting banded and patch farmland shelterbelt in Northeast China, and we analyzed the potential of applying it to the production of large-scale farmland shelterbelt products. Firstly, we classified banded and patch farmland shelterbelt under different sample window sizes using the improved Prototypical Network in the source domain study area to obtain the optimal sample window size and the optimal classification model. Secondly, fine-tuning transfer learning and learning from scratch directly were used to classify the banded and patch farmland shelterbelt in the target domain study area, respectively, to evaluate the extraction model’s migratability. The results showed that classification of farmland shelterbelt using the improved Prototypical Network is very effective, with the highest extraction accuracy under the 5 × 5 sample window; the accuracies of the banded and patch farmland shelterbelt are 92.16% and 90.91%, respectively. Using the fine-tuning transfer learning method in the target domain can classify the banded and patch farmland shelterbelt with high accuracy, above 95% and 89%, respectively. The proposed approach can provide new insight into farmland shelterbelt classification and farmland shelterbelt products obtained from freely accessible Sentinel-2 multispectral images. Full article
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Figure 1

Figure 1
<p>(<b>a</b>) Location of the study areas and the distribution of the sample points, (<b>b</b>) Fujin, (<b>c</b>) Fuyu, (<b>d</b>) Hailun, (<b>e</b>) Yi’an, (<b>f</b>) Youyi.</p>
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<p>Technical flowchart of this study.</p>
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<p>Overall classification framework of the improved Prototypical Network.</p>
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<p>Schematic diagram of the improved CutMix.</p>
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<p>Distribution map and localized zoomed map of banded and patch farmland shelterbelt in Fujin.</p>
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<p>Distribution map and localized zoomed map of banded and patch farmland shelterbelt in Hailun.</p>
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<p>Distribution map and localized zoomed map of banded and patch farmland shelterbelt in Youyi.</p>
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<p>Distribution map and localized zoomed map of banded and patch farmland shelterbelt in Yi’an.</p>
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<p>Distribution map and localized zoomed map of banded and patch farmland shelterbelt in Fuyu.</p>
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