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Search Results (881)

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Keywords = afforestation

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27 pages, 5359 KiB  
Article
Opportunities for the Early Diagnosis and Selection of Scots Pine with Potential Resistance to Root and Butt Rot Disease
by Valentyna Dyshko, Ivan Ustskiy, Piotr Borowik and Tomasz Oszako
Forests 2024, 15(10), 1789; https://doi.org/10.3390/f15101789 - 11 Oct 2024
Viewed by 346
Abstract
Pine stands affected by root and butt rot (Heterobasidion annosum s.l.) contain pines (Pinus sylvestris L.) that can survive for a long time without showing external symptoms of the disease (‘conditionally resistant’ refers to trees that survive without symptoms despite [...] Read more.
Pine stands affected by root and butt rot (Heterobasidion annosum s.l.) contain pines (Pinus sylvestris L.) that can survive for a long time without showing external symptoms of the disease (‘conditionally resistant’ refers to trees that survive without symptoms despite infection). The establishment of stands from the seeds of such trees can significantly increase the effectiveness of artificial afforestation. Since the growth and development of pine trees is determined to a certain extent by the number of cotyledons after seed germination, this article examines this trait in the progeny of trees that are potentially resistant and those that have already been attacked by root pathogens. The number of cotyledons and the resilience of trees is fascinating and not generally known. Presumably, the number of cotyledons can be linked to disease resistance based on increased vigour. Biologically, a larger area for carbon assimilation leads to better photosynthetic efficiency and the production of more assimilates (sugars) necessary to trigger defence processes in the event of infection. From an ecological point of view, this can give tree populations in areas potentially threatened by root system diseases a chance of survival. The aim of this study was to analyze the potential of using the number of cotyledons and other seedling characteristics to predict the resistance of trees to root and butt rot disease. The collected data show that the seedlings from the group of diseased trees exhibited lower growth rates and vigour. However, the seedlings from the group of potentially resistant trees are similar to the control, meaning the trees that show no disease symptoms because they have not come into contact with the pathogen. Our observations suggest that monitoring germinating cotyledons could serve as an early diagnostic tool to identify disease-resistant pines, although further research is needed. Full article
(This article belongs to the Section Forest Health)
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Figure 1
<p>Conceptual diagram of the idea of the reported experiment.</p>
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<p>Often one (<b>a</b>–<b>c</b>) or a group (<b>d</b>) of living, asyptomatic trees remains in the gap that has arisen in the stand. The cause of the death of the other trees is the fungus <span class="html-italic">Hetereobasidion</span> spp., whose fruiting bodies grow on the remaining stumps (<b>c</b>). The dead trees initially remain standing (<b>b</b>) and are then blown over by the wind (<b>c</b>,<b>e</b>).</p>
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<p>Photos of seeds and seedlings taken during the experiment. (<b>a</b>) Seeds counted and prepared for weighing. (<b>b</b>) Germinated seedlings in a Petri dish. (<b>c</b>) Seedlings prepared for measurements. (<b>d</b>) A single seedling.</p>
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<p>Weight of batches of 50 seeds compared to the treatment variant.</p>
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<p>Number of germinated seeds in lots of 100 from each of the considered trees versus the treatment variant.</p>
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<p>The average weight of a batch of 50 seeds collected from a tree compared to the proportion of germinated seeds. Ninety percent confidence ellipses are plotted as a guide.</p>
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<p>Mean number of cotyledons in seedlings germinated from trees from different experimental treatment categories. Visualisation of the variability of the mean values by tree from which the seeds were collected.</p>
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<p>Mean stem length of the germinated seedlings of trees belonging to different experimental treatment categories. Visualisation of the variability of the mean values according to the tree from which the seeds were collected.</p>
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<p>Mean root length of germinated seedlings of trees belonging to different experimental treatment categories. Visualisation of the variability of the mean values depending on the tree from which the seeds were collected.</p>
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<p>Mean needle length of germinated seedlings of trees belonging to different experimental treatment categories. Visualisation of the variability of the mean values according to the tree from which the seeds were collected.</p>
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<p>Mean ratio of stem/root length proportion of germinated seedlings of trees belonging to different experimental treatment categories. Visualisation of the variability of the mean values by tree from which the seeds were collected.</p>
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<p>Proportion of seedlings from seeds of a given tree compared to the number of developed cotyledons. Comparison between treatment groups.</p>
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<p>The ratio between stem and root length compared to the number of developed cotyledons in the seedling. Comparison between the treatment groups.</p>
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<p>Phases of mitosis in apical meristems of roots of tree seedlings with different resistance to <span class="html-italic">Heterobasidion</span> under a light microscope (100× magnification).</p>
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16 pages, 3114 KiB  
Article
Applicability of a Modified Gash Model for Artificial Forests in the Transitional Zone between the Loess Hilly Region and the Mu Us Sandy Land, China
by Xin Wang, Zhenqi Yang, Jianying Guo, Fucang Qin, Yabo Wang and Jiajun Ning
Sustainability 2024, 16(19), 8709; https://doi.org/10.3390/su16198709 - 9 Oct 2024
Viewed by 388
Abstract
Afforestation in the transitional zone between the loess hilly area and the Mu Us Sandy Land of China has reshaped the landscape and greatly affected eco-hydrological processes. Plantations are crucial for regulating local net rainfall inputs, thus making it necessary to quantify the [...] Read more.
Afforestation in the transitional zone between the loess hilly area and the Mu Us Sandy Land of China has reshaped the landscape and greatly affected eco-hydrological processes. Plantations are crucial for regulating local net rainfall inputs, thus making it necessary to quantify the closure loss of plantation species in drought and semi-arid areas. To quantify and model the canopy interception of these plantations, we conducted rainfall redistribution measurement experiments. Based on this, we used the modified Gash model to simulate their interception losses, and the model applicability across varying rainfall types was further compared and verified. Herein, Caragana korshinskii, Salix psammophila, and Pinus sylvestris plantations in the Kuye River mountain tract were chosen to measure the precipitation distribution from May to October (growing season). The applicability of a modified Gash model for different stands was then evaluated using the assessed data. The results showed that the canopy interception characteristics of each typical plantation were throughfall, interception, and stemflow. The relative error of canopy interception of C. korshinskii simulated by the modified Gash model was 8.79%. The relative error of simulated canopy interception of S. psammophila was 4.19%. The relative error of canopy interception simulation of P. sylvestris was 13.28%, and the modified Gash model had good applicability in the Kuye River Basin. The modified Gash model has the greatest sensitivity to rainfall intensity among the parameters of the C. korshinskii and S. psammophila forest. The sensitivity of P. sylvestris in the modified Gash model is that the canopy cover has the greatest influence, followed by the mean rainfall intensity. Our results provide a scientific basis for the rational use of water resources and vegetation restoration in the transitional zone between the loess hilly region and the Mu Us Sandy Land. This study is of import for the restoration and sustainability of fragile ecosystems in the region. Full article
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<p>Map of the study area.</p>
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<p>Rainfall characteristics in the study area during the test period.</p>
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<p>Individual rainfall amount and associated rainfall intensity during the experimental period for <span class="html-italic">Caragana korshinskii</span> (<b>a</b>), <span class="html-italic">Salix psammophila</span> (<b>b</b>), and <span class="html-italic">Pinus sylvestris</span> (<b>c</b>).</p>
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<p>Throughfall, stemflow, and interception rates of the three typical vegetation types.</p>
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<p>Relationship between rainfall amount and net rainfall outside a forest during a typical vegetation experiment.</p>
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<p>Simulation results of the modified Gash model.</p>
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<p>Sensitivity analysis of the revised Gash model parameters.</p>
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18 pages, 5115 KiB  
Article
Drainage and Afforestation More Strongly Affect Soil Microbial Composition in Fens than Bogs of Subtropical Moss Peatlands
by Putao Zhang, Junheng Yang, Haijun Cui, Weifeng Song, Yingying Liu, Xunxun Shi, Xiaoting Bi and Suyao Yuan
Sustainability 2024, 16(19), 8621; https://doi.org/10.3390/su16198621 - 4 Oct 2024
Viewed by 608
Abstract
Subtropical moss peatlands have important ecological functions, and their protection and restoration are urgent. The lack of understanding of the biogeochemical changes in subtropical moss peatlands after human disturbance, particularly regarding their underground ecological changes, limits the efforts towards their protection and restoration. [...] Read more.
Subtropical moss peatlands have important ecological functions, and their protection and restoration are urgent. The lack of understanding of the biogeochemical changes in subtropical moss peatlands after human disturbance, particularly regarding their underground ecological changes, limits the efforts towards their protection and restoration. In this study, typical subtropical moss peatlands and the Cryptomeria swamp forest (CSF) formed by long-term (more than 20 years) drainage and afforestation in the Yunnan–Guizhou Plateau of China were selected as the research sites. Moreover, 16S rRNA high-throughput sequencing technology was used to study the differences in soil bacterial community diversity and composition among a natural Sphagnum fen (SF), Polytrichum bog (PB), and CSF to explore the effects of drainage and afforestation on different types of moss peatlands and its mechanism combined with soil physicochemical properties. Results showed that (1) drainage and afforestation significantly reduced the α diversity of soil bacterial communities in SF while significantly increasing the α diversity of soil bacterial communities in PB. Soil bacterial communities of SF had the highest α diversity and had many unique species or groups at different taxonomic levels. (2) The impact of drainage and afforestation on the soil bacterial community composition in SF was significantly higher than that in PB. Drainage and afforestation caused significant changes in the composition and relative abundance of dominant groups of soil bacteria in SF at different taxonomic levels, such as significantly reducing the relative abundance of Proteobacteria, significantly increasing the relative abundance of Acidobacteria, and significantly reducing the ratio of Proteobacteria to Acidobacteria, but did not have a significant impact on the corresponding indicators of PB. The changes in the ratio of Proteobacteria to Acidobacteria may reflect changes in the trophic conditions of peatlands. (3) Soil moisture content, available phosphorus content, and pH were key driving factors for changes in soil bacterial community composition and diversity, which should be paid attention to in the restoration of moss peatlands. This study provides insights into the protection and restoration of subtropical moss peatlands. Full article
(This article belongs to the Special Issue Soil Microorganisms, Plant Ecology and Sustainable Restoration)
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<p>Comparison of soil physicochemical properties among <span class="html-italic">Sphagnum</span> fen (SF), <span class="html-italic">Polytrichum</span> bog (PB), and <span class="html-italic">Cryptomeria</span> swamp forest (CSF). TC—soil total carbon content (<b>A</b>); TN—soil total nitrogen content (<b>B</b>); pH—soil pH (<b>C</b>); AP—soil available phosphorus content (<b>D</b>); NO<sub>3</sub><sup>−</sup>-N—soil nitrate nitrogen content (<b>E</b>); NH<sub>4</sub><sup>+</sup>-N—soil ammonium nitrogen content (<b>F</b>); SWW—soil weight water content (<b>G</b>); SBD—soil bulk density (<b>H</b>). Error bars indicate the standard errors (<span class="html-italic">n</span> = 3). Lowercase letters (a, b, c) represent significantly different values of the studied parameter with a 95% confidence interval, confirmed by ANOVA with subsequent LSD comparisons.</p>
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<p>Comparison of soil bacterial α diversity among <span class="html-italic">Sphagnum</span> fen (SF), <span class="html-italic">Polytrichum</span> bog (PB), and <span class="html-italic">Cryptomeria</span> swamp forest (CSF). Sobs—the observed richness (<b>A</b>); ACE—the ACE estimator (<b>B</b>); Chao—the Chao1 estimator (<b>C</b>); Shannon—the Shannon diversity index (<b>D</b>); Simpson—the Simpson diversity index (<b>E</b>); Pd—phylogenetic diversity (<b>F</b>); Shannoneven—a Shannon index-based measure of evenness (<b>G</b>); Simpsoneven—a Simpson index-based measure of evenness (<b>H</b>); Coverage—the Good’s coverage <b>(I</b>). Sobs, ACE, and Chao reflecting on community richness; Shannon, Simpson, and Pd reflecting on community diversity; Shannoneven and Simpsoneven reflecting on community evenness; and Coverage reflecting on community coverage. Error bars indicate the standard errors (<span class="html-italic">n</span> = 3). Lowercase letters (a, b, c) represent significantly different values of the studied parameter with a 95% confidence interval, confirmed by ANOVA with subsequent LSD comparisons.</p>
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<p>Variations of soil bacterial composition among <span class="html-italic">Sphagnum</span> fen (SF), <span class="html-italic">Polytrichum</span> bog (PB), and <span class="html-italic">Cryptomeria</span> swamp forest (CSF) at phylum (<b>A</b>–<b>C</b>), class (<b>D</b>–<b>F</b>), family (<b>G</b>–<b>I</b>), and genus levels (<b>J</b>–<b>L</b>). (1) Comparison of soil bacterial composition among different types of sites by NMDS based on Bray–Curtis distance (<b>A</b>,<b>D</b>,<b>G</b>,<b>J</b>). (2) The number of shared and unique taxa across different types of sites (<b>B</b>,<b>E</b>,<b>H</b>,<b>K</b>). (3) Comparison of the dissimilarities of soil bacterial communities between different types of sites (<b>C</b>,<b>F</b>,<b>I</b>,<b>L</b>). Each box plot represents the maximum, minimum, 75th, and 25th quartiles, respectively; the line of each box plot represents the median, and the red point of each box plot represents the mean (<span class="html-italic">n</span> = 9). Lowercase letters (a, b, c) represent significantly different values of the studied parameter with a 95% confidence interval, confirmed by ANOVA with subsequent LSD comparisons.</p>
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<p>Indicator group analysis of bacterial communities in <span class="html-italic">Sphagnum</span> fen (SF), <span class="html-italic">Polytrichum</span> bog (PB), and <span class="html-italic">Cryptomeria</span> swamp forest (CSF) with LDA SCORE &gt; 3.5.</p>
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<p>Comparison of the relative abundance of major groups of soil bacteria in <span class="html-italic">Sphagnum</span> fen (SF), <span class="html-italic">Polytrichum</span> bog (PB), and <span class="html-italic">Cryptomeria</span> swamp forest (CSF) at phylum (<b>A</b>), class (<b>B</b>), family (<b>C</b>), and genus (<b>D</b>) levels. The main groups of soil bacteria were composed of the top ten groups in the relative abundance of each type of site. Error bars indicate the standard errors (<span class="html-italic">n</span> = 3). Lowercase letters (a, b, c) represent significantly different values of the studied parameter with a 95% confidence interval, confirmed by ANOVA with subsequent LSD comparisons.</p>
Full article ">Figure 5 Cont.
<p>Comparison of the relative abundance of major groups of soil bacteria in <span class="html-italic">Sphagnum</span> fen (SF), <span class="html-italic">Polytrichum</span> bog (PB), and <span class="html-italic">Cryptomeria</span> swamp forest (CSF) at phylum (<b>A</b>), class (<b>B</b>), family (<b>C</b>), and genus (<b>D</b>) levels. The main groups of soil bacteria were composed of the top ten groups in the relative abundance of each type of site. Error bars indicate the standard errors (<span class="html-italic">n</span> = 3). Lowercase letters (a, b, c) represent significantly different values of the studied parameter with a 95% confidence interval, confirmed by ANOVA with subsequent LSD comparisons.</p>
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<p>Redundancy analysis showing the relationship between soil physicochemical properties and major groups of soil bacterial communities in all types of sites at phylum (<b>A</b>), class (<b>B</b>), family (<b>C</b>), and genus (<b>D</b>) levels. SF—<span class="html-italic">Sphagnum</span> fen; PB—<span class="html-italic">Polytrichum</span> bog; CSF—<span class="html-italic">Cryptomeria</span> swamp forest.</p>
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26 pages, 12307 KiB  
Article
Research on the Performance and Control Strategy of Electro-Hydraulic Servo System for Selective Hole Digging Tree Planter
by Binhai Zhu, Jiuqing Liu, Hang Yu, Li Yu, Zhenli Wang, Huan Zhou and Chunmei Yang
Forests 2024, 15(10), 1744; https://doi.org/10.3390/f15101744 - 2 Oct 2024
Viewed by 489
Abstract
Compared to agricultural environments, afforestation sites are more complex, often presenting issues such as undulating and uneven terrain. These conditions lead to instability in hole digging depth and plant spacing during continuous movement, and the hole shape may not meet expectations. Additionally, the [...] Read more.
Compared to agricultural environments, afforestation sites are more complex, often presenting issues such as undulating and uneven terrain. These conditions lead to instability in hole digging depth and plant spacing during continuous movement, and the hole shape may not meet expectations. Additionally, the hydraulic system exhibits slow response speed and long steady-state time, affecting the quality of sapling planting. To address these issues, this paper designs an intelligent planting control system for intermittent hole digging under continuous dynamic movement, based on a large tree planter. The focus is on studying the dynamic accuracy of the hole digging cylinder to resolve the instability of plant spacing and planting depth in actual planting processes. Firstly, a motion trajectory model of the intermittent hole digging mechanism is established to obtain the relationship between the displacement trajectory of the rotating cutter and the displacements of the floating cylinder and the hole digging cylinder. Secondly, a mathematical model of the electro-hydraulic servo system is established to control the dynamic accuracy of the hole digging operation. Finally, a Simulink simulation model of the system is established to analyze the performance indicators of the hydraulic system during operation using step and sinusoidal excitation signals. The test results show that the displacement of the hydraulic piston rod can ensure a linear extension trend within the range of 0 to 0.4 m, and the extension distance of the hole digging cylinder in the planting system is 0 to 0.35 m, ensuring linear change within this stroke. When the system’s extension command is 1 V, the actual output is 0.6 m, with a relative error of less than 10% compared to the simulation value, indicating that the control strategy can effectively improve the dynamic performance of the system. When the hydraulic system is in a steady-state extension state at 50 to 58.6 s, the relative error with the simulation value is 7.3%, meeting the “double ten indicators” requirement. The research results clearly verify the superior performance of the proposed intelligent control system, and the proposed control strategy has great potential in practical applications, promising to improve afforestation quality by stabilizing planting spacing and planting depth. Full article
(This article belongs to the Special Issue New Development of Smart Forestry: Machine and Automation)
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<p>Three-dimensional modeling of a tree planting machine.</p>
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<p>Simplified planar linkage mechanism.</p>
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<p>Working principle of the hydraulic actuator for digging holes.</p>
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<p>Values of <span class="html-italic">C<sub>r</sub></span>, <span class="html-italic">C<sub>rc</sub></span>, <span class="html-italic">C<sub>s</sub></span>, and <span class="html-italic">C<sub>sc</sub></span> time domain curves.</p>
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<p>(<b>a</b>). <span class="html-italic">C<sub>r</sub></span>, <span class="html-italic">C<sub>rc</sub></span> step response curves; (<b>b</b>). <span class="html-italic">C<sub>s</sub></span>, <span class="html-italic">C<sub>sc</sub></span> step response curves. Time domain curves of the system are analyzed for the conditions of <span class="html-italic">C<sub>r</sub></span>, <span class="html-italic">C<sub>rc</sub></span>, <span class="html-italic">C<sub>s</sub></span>, and <span class="html-italic">C<sub>sc</sub></span>.</p>
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<p>Simplified Simulink simulation model of the system.</p>
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<p>Simulink simulation model of asymmetric hydraulic system.</p>
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<p>(<b>a</b>). Step response curve; (<b>b</b>). Sine response curve. Time domain curves of the step and sinusoidal response.</p>
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<p>(<b>a</b>). Simulink simulation model; (<b>b</b>). LQR code program. Simulation model of hydraulic system based on LQR linear state feedback control with feedforward.</p>
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<p>Step response of piston rod extension system.</p>
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<p>Step response of piston rod retraction system.</p>
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<p>(<b>a</b>). The 0.1 Hz sinusoidal signal response curve; (<b>b</b>). 0.5 Hz sinusoidal signal response curve; (<b>c</b>). 1 Hz sinusoidal signal response curve; (<b>d</b>). 2 Hz sinusoidal signal response curve. Sine response curve of the system.</p>
Full article ">Figure 12 Cont.
<p>(<b>a</b>). The 0.1 Hz sinusoidal signal response curve; (<b>b</b>). 0.5 Hz sinusoidal signal response curve; (<b>c</b>). 1 Hz sinusoidal signal response curve; (<b>d</b>). 2 Hz sinusoidal signal response curve. Sine response curve of the system.</p>
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<p>Composition structure of the electro-hydraulic position servo system.</p>
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<p>Upper computer experiment model.</p>
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<p>(<b>a</b>). Response curve of the hydraulic system during extension; (<b>b</b>). response curve of the hydraulic system during retraction. Step response curve.</p>
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<p>(<b>a</b>). Response curve of the hydraulic system during extension; (<b>b</b>). response curve of the hydraulic system during retraction. Step response curve.</p>
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<p>(<b>a</b>). The 0.5 Hz sinusoidal response curve; (<b>b</b>). 2 Hz sinusoidal response curve. Sinusoidal response curve.</p>
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24 pages, 3086 KiB  
Article
Potential and Investment Attractiveness of Implementing Climate Projects on Disturbed Lands
by Svetlana S. Morkovina, Nataliya V. Yakovenko, Sergey S. Sheshnitsan, Denis Kuznetsov, Anton Shashkin, Alexander Tretyakov and Julia Stepanova
Sustainability 2024, 16(19), 8562; https://doi.org/10.3390/su16198562 - 2 Oct 2024
Viewed by 497
Abstract
Forest restoration projects can be categorized as climate projects, investments in the implementation of which exceed the investment costs of forest-climate projects, which reduces their attractiveness to investors. An algorithm for assessing investment costs of climate reforestation projects on disturbed lands has been [...] Read more.
Forest restoration projects can be categorized as climate projects, investments in the implementation of which exceed the investment costs of forest-climate projects, which reduces their attractiveness to investors. An algorithm for assessing investment costs of climate reforestation projects on disturbed lands has been developed. The potential of territories for the implementation of such project initiatives is available in all regions of Russia and amounts to more than 381 thousand hectares. For five studied polygons of disturbed lands (Kuzbass basin, Moscow basin, Western Siberia basin, as well as basins of Chelyabinsk and Belgorod Regions), the aggregated costs for the implementation of measures to create carbon-depositing plantations and ground cover were calculated. Investment costs for restoration of 1 hectare of disturbed land under the climate project vary from 82.6 thousand rubles to 116.9 thousand rubles. Cost analysis shows that the carbon intensity of investment in such projects on disturbed lands is quite high (Ccii > 1.0). The highest investment potential is observed in the Kuzbass basin, where Ccii is 2.01. To organize and implement the afforestation project on disturbed lands of the Kemerovo Region, investments in the amount of 66.7 thousand rubles/ha for capital expenditures and 24.7 thousand rubles/ha for current expenses will be required. The payback period of such an investment project, taking into account the discount rate, is 13.1 years, and during the study period (20 years) the income from the project will cover 228% of the spent funds. These data confirm that the investment potential of forest-climatic projects on disturbed lands is quite high. Full article
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<p>Disturbed lands of the subjects of the Russian Federation.</p>
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<p>Areas of disturbed lands by categories as of 1 December 2023, thousand ha. (1)—agricultural lands; (2)—lands of the forest fund; (3)—lands of industry and other special purposes; (4)—lands of specially protected territories and facilities; (5)—lands of reserves and settlements.</p>
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<p>Dynamics of disturbed land area for 2019–2023 (thousand ha). (1)—agricultural lands; (2)—lands of the forest fund; (3)—lands of industry and other special purposes; (4)—lands of specially protected territories and facilities; (5)—lands of reserves and settlements.</p>
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<p>Growth dynamics of disturbed lands area on agricultural lands for the period 2019–2023, thousand ha.</p>
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<p>Growth dynamics of disturbed land area on the forest fund lands, for the period 2019–2023, thousand ha.</p>
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<p>Virtual clustering of disturbed land potential suitable for climate-smart afforestation projects.</p>
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22 pages, 9821 KiB  
Article
Farmers’ Willingness to Accept Afforestation in Farming Land and Its Influencing Factors in Fragile Landscapes Based on the Contingent Valuation Method
by Sharada Karki and Shigehiro Yokota
Forests 2024, 15(10), 1742; https://doi.org/10.3390/f15101742 - 2 Oct 2024
Viewed by 512
Abstract
Afforestation (AF) in farmland has been widely used as an alternative and sustainable land-use practice to address socioeconomic and environmental challenges. The aim of this study is to estimate farmers’ willingness to accept (WTA) compensation and land, both of which are equally significant [...] Read more.
Afforestation (AF) in farmland has been widely used as an alternative and sustainable land-use practice to address socioeconomic and environmental challenges. The aim of this study is to estimate farmers’ willingness to accept (WTA) compensation and land, both of which are equally significant for policymakers to ensure the effective implementation of AF and achieve desired outcomes. This topic has not been sufficiently explored in previous research. This study focused on areas characterized by insecure farming conditions, backward economies, and fragile landscapes, where farmers are generally unfamiliar with AF or compensation for ecosystem services under payment for ecosystem services programs. It assessed their attitudes towards the WTA AF, compensation, and land as an alternative practice, which remains under-researched. This is crucial for designing effective AF programs in the future to improve livelihood and enhance the quantity and quality of the environment. This study used the contingent valuation method to estimate the minimum WTA compensation and maximum land for the forgone loss and alternative land-use practices. A questionnaire survey was conducted in Hupsekot municipality, Nepal, with 232 farmer households. The ordinal logistic regression model was used to analyze influencing factors of WTA compensation and land. The result showed that farmers’ average WTA compensation was NPR 1268.67 (USD 9.76)/Kattha/year, with 2.64 Kattha land available for AF. The factors, including socioeconomic characters and attitudes toward the environmental situation and forests, significantly influenced WTA values and provided potential target factors to achieve maximum AF land within a lower budget. Full article
(This article belongs to the Section Forest Economics, Policy, and Social Science)
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<p>Data collection sites within the upstream area of Hupsekot rural municipality.</p>
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<p>Respondents’ awareness of environmental degradation level and the importance of forests in managing degradation (%, N = 232).</p>
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<p>The forest needs and satisfaction level for respondents (%, N = 232).</p>
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<p>Respondents’ WTA land for AF (based on respondents who showed WTA AF; N = 163).</p>
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<p>Respondents’ reasons for unwillingness to accept AF (N = 69).</p>
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<p>River cutting and environmental risk scenario in Hupsekot (pictures are taken from Google Maps).</p>
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<p>The importance of implementing afforestation as an alternative land-use practice in agricultural areas and its potential benefits for upstream (fragile) landscapes, based on the concept of payments for ecosystem services (PES).</p>
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21 pages, 2415 KiB  
Article
Factors Influencing Carbon Emission and Low-Carbon Development Levels in Shandong Province: Method Analysis Based on Improved Random Forest Partial Least Squares Structural Equation Model and Entropy Weight Method
by Yingjie Zhu, Yinghui Guo, Yongfa Chen, Jiageng Ma and Dan Zhang
Sustainability 2024, 16(19), 8488; https://doi.org/10.3390/su16198488 - 29 Sep 2024
Viewed by 648
Abstract
Comprehensively clarifying the influencing factors of carbon emissions is crucial to realizing carbon emission reduction targets in China. To address this issue, this paper develops a four-level carbon emission influencing factor system from six perspectives: population, economy, energy, water resources, main pollutants, and [...] Read more.
Comprehensively clarifying the influencing factors of carbon emissions is crucial to realizing carbon emission reduction targets in China. To address this issue, this paper develops a four-level carbon emission influencing factor system from six perspectives: population, economy, energy, water resources, main pollutants, and afforestation. To analyze how these factors affect carbon emissions, we propose an improved partial least squares structural equation model (PLS-SEM) based on a random forest (RF), named RF-PLS-SEM. In addition, the entropy weight method (EWM) is employed to evaluate the low-carbon development level according to the results of the RF-PLS-SEM. This paper takes Shandong Province as an example for empirical analysis. The results demonstrate that the improved model significantly improves accuracy from 0.8141 to 0.9220. Moreover, water resources and afforestation have relatively small impacts on carbon emissions. Primary and tertiary industries are negative influencing factors that inhibit the growth of carbon emissions, whereas total energy consumption, the volume of wastewater discharged and of common industrial solid waste are positive and direct influencing factors, and population density is indirect. In particular, this paper explores the important role of fisheries in reducing carbon emissions and discusses the relationship between population aging and carbon emissions. In terms of the level of low-carbon development, the assessment system of carbon emission is constructed from four dimensions, namely, population, economy, energy, and main pollutants, showing weak, basic, and sustainable stages of low-carbon development during the 1997–2012, 2013–2020, and 2021–2022 periods, respectively. Full article
(This article belongs to the Special Issue Energy Sources, Carbon Emissions and Economic Growth)
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Graphical abstract

Graphical abstract
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<p>Carbon emissions of 34 provinces in China in 2021. Source of data: the carbon emission data for 30 provinces in China (excluding Hong Kong, Macao, Taiwan, and Tibet Autonomous Region) in 2021 were obtained from the China Emission Accounts and Datasets (CEADs), and the data for Hong Kong, Macao, Taiwan, and the Tibet Autonomous Region were obtained from the Environment and Ecology Bureau, the Environmental Protection Bureau of the Macao Special Administrative Region, the BIOSIS Previews database and the China Tibet News Network, respectively. The green line in the figure represents the Qinling-Huaihe River demarcation line, and the blue line, and the blue lines on the map represent islands or coastlines.</p>
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<p>Carbon emission empirical indicator system.</p>
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<p>Feature screening results for RF.</p>
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<p>The system of terminal indicators.</p>
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<p>Latent variables path analysis of carbon emissions. Note: the paths representing positive influencing factors are depicted as solid black lines, whereas the paths for negative influencing factors are shown as red dashed lines.</p>
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<p>Path analysis of disaggregated economic indicators and carbon emissions and their influencing factors. Note: the paths representing positive influencing factors are depicted as solid black lines, whereas those for negative influencing factors are shown as red dashed lines.</p>
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<p>Low-carbon development level score by subsystem.</p>
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<p>Overall score for the level of low-carbon development. Note: The blue line graph represents the growth rate of the low-carbon development level score.</p>
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14 pages, 2055 KiB  
Article
Morpho-Physiological and Biochemical Responses in Prosopis laevigata Seedlings to Varied Nitrogen Sources
by Erickson Basave-Villalobos, Luis Manuel Valenzuela-Núñez, José Leonardo García-Rodríguez, Homero Sarmiento-López, José Luis García-Pérez, Celi Gloria Calixto-Valencia and José A. Sigala
Nitrogen 2024, 5(4), 857-870; https://doi.org/10.3390/nitrogen5040055 - 28 Sep 2024
Viewed by 582
Abstract
Nitrogen (N) fertilization promotes morphofunctional attributes that enhance plant performance under stress conditions, but the amount and form supplied modify the magnitude of plant responses. We assessed several morpho-physiological and biochemical responses of Prosopis laevigata seedlings to a high supply of N, provided [...] Read more.
Nitrogen (N) fertilization promotes morphofunctional attributes that enhance plant performance under stress conditions, but the amount and form supplied modify the magnitude of plant responses. We assessed several morpho-physiological and biochemical responses of Prosopis laevigata seedlings to a high supply of N, provided as either inorganic (NH4NO3) or organic (amino acids). Such N treatments were applied on four-month-old seedlings as a supplement of 90 mg N to a regular supply of 274 mg N plant−1. Nitrogen supply modified biomass allocation patterns between leaves and roots regardless of N form. Increased N input decreased photosynthetic capacity, even when plants had high internal N reserves. Organic N fertilization reduced the N use efficiency, but increased leaf and root amino acid concentrations. Proteins accumulated in stems in plants receiving inorganic N, while the organic N increased leaf proteins. High N supply promoted root starch accumulation irrespective of N form. Nitrogen supply did not directly influence plants’ regrowth capacity. Still, resprouting was correlated to initial root-to-shoot ratios and root starch, confirming the importance of roots as storage reserves of starch for recovering biomass after browsing. These findings have practical implications for designing nutritional management strategies in nurseries to improve seedling performance in afforestation efforts. Full article
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<p>Changes in biomass allocation patterns in <span class="html-italic">Prosopis laevigata</span> seedlings fertilized with additional N from two sources, inorganic N (NH<sub>4</sub>NO<sub>3</sub>) and organic N (amino acids), relative to control plants with regular N supply. Values presented are means with 95% confidence intervals. Symbols on each mean indicate the statistical comparison of fertilization treatments against the control (ns = not significant, ** <span class="html-italic">p</span> &lt; 0.01).</p>
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<p>Nitrogen concentration (<b>A</b>), N content (<b>B</b>), and N use efficiency (<b>C</b>) in <span class="html-italic">Prosopis laevigata</span> seedlings in response to inorganic (NH<sub>4</sub>NO<sub>3</sub>) and organic (amino acids) nitrogen fertilization. Data are means ± 1 SE. Horizontal square brackets indicate the statistical comparison of fertilization treatments against the control (ns = non-significant, ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001).</p>
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<p>Amino acid concentration (<b>A</b>), proteins (<b>B</b>), starch (<b>C</b>), and soluble total sugars (<b>D</b>) in leaf, stem, and root tissues in <span class="html-italic">Prosopis laevigata</span> seedlings in response to inorganic (NH<sub>4</sub>NO<sub>3</sub>) and organic (amino acids) nitrogen fertilization. Data are means ± 1 SE. Horizontal square brackets indicate a comparison between treatments and control. Statistical significance: ns = non-significant, ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001) fertilization treatments to control.</p>
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<p>Length of the dominant shoot after pruning in plants of <span class="html-italic">Prosopis laevigata</span> in response to inorganic (NH<sub>4</sub>NO<sub>3</sub>) and organic (amino acids) nitrogen fertilization. Data are means ± 1 SE.</p>
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<p>Relationship of sprout mass with the above-grown mass prior to pruning (<b>A</b>) and root-to-shoot ratio (<b>B</b>), and relationship of the number of new sprouts with starch concentration in the shoot (<b>C</b>) and root (<b>D</b>) in plants of <span class="html-italic">Prosopis laevigata</span> fertilized with inorganic (NH<sub>4</sub>NO<sub>3</sub>) and organic (amino acids) nitrogen. Data are means. Lines and shades area represent predicted values and a confident Interval of 95%. Values of independent variables (<span class="html-italic">x</span>-axis) were measured before pruning.</p>
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21 pages, 1984 KiB  
Article
Prediction of Energy Consumption and Carbon Dioxide Emissions in Gansu Province of China under the Background of “Double Carbon”
by Mingchen Duan and Yi Duan
Energies 2024, 17(19), 4842; https://doi.org/10.3390/en17194842 - 27 Sep 2024
Viewed by 414
Abstract
Gansu Province in China has the characteristics of an underdeveloped economy, low forest carbon sink, and rich non-fossil energy, making it a typical area for research to achieve the “double carbon” target. In this paper, the primary energy consumption and carbon emissions and [...] Read more.
Gansu Province in China has the characteristics of an underdeveloped economy, low forest carbon sink, and rich non-fossil energy, making it a typical area for research to achieve the “double carbon” target. In this paper, the primary energy consumption and carbon emissions and their development trends in Gansu Province during the “double carbon” target period were predicted by the fixed-base energy consumption elasticity coefficient method, and the possibility of achieving the “double carbon” target in Gansu Province was explored. In the three hypothetical scenarios, it was estimated that the total primary energy consumption of Gansu Province will be 91.9–94.81 million tons of standard coal by 2030 and 99.35–110.76 million tons of standard coal by 2060. According to the predicted share of different energy consumption in Gansu Province, the CO2 emissions of Gansu Province in the three scenarios were calculated and predicted to be between 148.60 and 153.31 million tons in 2030 and 42.10 and 46.93 million tons in 2060. The study suggests that Gansu Province can reach the carbon peak before 2030 in the hypothetical scenarios. However, to achieve the goal of carbon neutrality by 2060, it was proposed that, in addition to increasing carbon sinks by afforestation, it is also necessary to increase the share of non-fossil energy. As long as the share is increased by 0.3% on the basis of 2030, the goal of carbon neutrality by 2060 in Gansu Province can be achieved. The results show that the increase in the share of non-fossil energy consumption is the most important way to achieve the goal of carbon neutrality in Gansu Province, and it also needs to be combined with the optimization of industrial structure and improvement of technological progress. Based on the research results, some countermeasures and suggestions are put forward to achieve the goal of carbon neutrality in Gansu Province. Full article
(This article belongs to the Special Issue Advances in Energy Transition to Achieve Carbon Neutrality)
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<p>GDP and energy consumption in Gansu Province during 2005–2021. The GDP data in <a href="#energies-17-04842-f001" class="html-fig">Figure 1</a> is calculated at current prices with included price increases.</p>
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<p>Growth rate of GDP and energy consumption in Gansu Province during 2005–2021.</p>
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<p>Energy consumption (<b>a</b>) and GDP (<b>b</b>) of different industries in Gansu Province during 2005–2021. The GDP data in <a href="#energies-17-04842-f003" class="html-fig">Figure 3</a>b is calculated at current prices with included price increases.</p>
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<p>Growth rate of energy consumption per unit GDP (<b>a</b>) and energy consumption per ten thousand yuan GDP (<b>b</b>) in Gansu Province during 2005–2021.</p>
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<p>(<b>a</b>,<b>b</b>) Production and consumption of different energy sources in Gansu Province during 2005–2021.</p>
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<p>Fixed-base energy consumption elasticity coefficient and its prediction in Gansu Province.</p>
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<p>Share and its prediction of different energy consumption in Gansu Province.</p>
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<p>Share and its prediction of non-fossil energy and fossil energy consumption in Gansu Province.</p>
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<p>CO<sub>2</sub> emission and its prediction in Gansu Province under different scenarios.</p>
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24 pages, 15190 KiB  
Article
Spatiotemporal Variation and Prediction of Carbon Storage in Terrestrial Ecosystems at Multiple Development Stages in Beijing City Based on the Plus and Integrated Valuation of Ecosystem Services and Tradeoffs Models
by Peian Wang, Chen Liu and Linlin Dai
Land 2024, 13(9), 1544; https://doi.org/10.3390/land13091544 - 23 Sep 2024
Viewed by 449
Abstract
Terrestrial ecosystems play a critical role in the global carbon cycle, and their carbon sequestration capacity is vital for mitigating the impacts of climate change. Changes in land use and land cover (LULC) dynamics significantly alter this capacity. This study scrutinizes the LULC [...] Read more.
Terrestrial ecosystems play a critical role in the global carbon cycle, and their carbon sequestration capacity is vital for mitigating the impacts of climate change. Changes in land use and land cover (LULC) dynamics significantly alter this capacity. This study scrutinizes the LULC evolution within the Beijing metropolitan region from 1992 to 2022, evaluating its implications for ecosystem carbon storage. It also employs the Patch-Generating Land Use Simulation (PLUS) model to simulate LULC patterns under four scenarios for 2035: an Uncontrolled Scenario (UCS), a Natural Evolution Scenario (NES), a Strict Control Scenario (SCS), and a Reforestation and Wetland Expansion Scenario (RWES). The InVEST model is concurrently used to assess and forecast ecosystem carbon storage under each scenario. Key insights from the study are as follows: (1) from 1992 to 2022, Beijing’s LULC exhibited a phased developmental trajectory, marked by an expansion of urban and forested areas at the expense of agricultural land; (2) concurrently, the region’s ecosystem carbon storage displayed a fluctuating trend, peaking initially before declining, with higher storage in the northwest and lower in the central urban zones; (3) by 2035, ecosystem carbon storage is projected to decrease by 1.41 Megatons under the UCS, decrease by 0.097 Megatons under the NES, increase by 1.70 Megatons under the SCS, and increase by 11.97 Megatons under the RWES; and (4) the study underscores the efficacy of policies curtailing construction land expansion in Beijing, advocating for sustained urban growth constraints and intensified afforestation initiatives. This research reveals significant changes in urban land use types and the mechanisms propelling these shifts, offering a scientific basis for comprehending LULC transformations in Beijing and their ramifications for ecosystem carbon storage. It further provides policymakers with substantial insights for the development of strategic environmental and urban planning initiatives. Full article
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<p>Location of Beijing.</p>
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<p>The technology roadmap of this study.</p>
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<p>The spatial distribution of Beijing’s LULC types in representative years.</p>
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<p>Spatial changes in carbon storage in Beijing from 1992 to 2022.</p>
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<p>Prediction of carbon storage in Beijing by 2035 under 4 scenarios (MT).</p>
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<p>Prediction of the spatial distribution of carbon storage under 4 scenarios.</p>
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<p>Comparison of carbon storage in 2035 and 2017 under 4 scenarios.</p>
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<p>Spatial change of carbon storage in Beijing in 2035 under Strict Control Scenario.</p>
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<p>The contribution of driving factors to the expansion of construction land.</p>
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<p>(<b>a</b>) Expansion potential of construction land (calculated based on development trends from 2011 to 2017, Uncontrolled Scenario); (<b>b</b>) Expansion potential of construction land (calculated based on development trends from 2017 to 2020, other scenarios).</p>
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22 pages, 6833 KiB  
Article
Identification of Spatial Distribution of Afforestation, Reforestation, and Deforestation and Their Impacts on Local Land Surface Temperature in Yangtze River Delta and Pearl River Delta Urban Agglomerations of China
by Zhiguo Tai, Xiaokun Su, Wenjuan Shen, Tongyu Wang, Chenfeng Gu, Jiaying He and Chengquan Huang
Remote Sens. 2024, 16(18), 3528; https://doi.org/10.3390/rs16183528 - 23 Sep 2024
Viewed by 562
Abstract
Forest change affects local and global climate by altering the physical properties of the land surface. Accurately assessing urban forest changes in local land surface temperature (LST) is a scientific and crucial strategy for mitigating regional climate change. Despite this, few studies have [...] Read more.
Forest change affects local and global climate by altering the physical properties of the land surface. Accurately assessing urban forest changes in local land surface temperature (LST) is a scientific and crucial strategy for mitigating regional climate change. Despite this, few studies have attempted to accurately characterize the spatial and temporal pattern of afforestation, reforestation, and deforestation to optimize their effects on surface temperature. We used the China Land Cover Dataset and knowledge criterion-based spatial analysis model to map urban forestation (e.g., afforestation and reforestation) and deforestation. We then analyzed the impacts of these activities on LST from 2010 to 2020 based on the moving window strategy and the spatial–temporal pattern change analysis method in the urban agglomerations of the Yangtze River Delta (YRD) and Pearl River Delta (PRD), China. The results showed that forest areas declined in both regions. Most years, the annual deforestation area is greater than the yearly afforestation areas. Afforestation and reforestation had cooling effects of −0.24 ± 0.19 °C and −0.47 ± 0.15 °C in YRD and −0.46 ± 0.10 °C and −0.86 ± 0.11 °C in PRD. Deforestation and conversion of afforestation to non-forests led to cooling effects in YRD and warming effects of 1.08 ± 0.08 °C and 0.43 ± 0.19 °C in PRD. The cooling effect of forests is more evident in PRD than in YRD, and it is predominantly caused by reforestation. Moreover, forests demonstrated a significant seasonal cooling effect, except for December in YRD. Two deforestation activities exhibited seasonal warming impacts in PRD, mainly induced by deforestation, while there were inconsistent effects in YRD. Overall, this study provides practical data and decision-making support for rational urban forest management and climate benefit maximization, empowering policymakers and urban planners to make informed decisions for the benefit of their communities. Full article
(This article belongs to the Section Forest Remote Sensing)
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<p>An overview map of the study area.</p>
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<p>CLCD-based land cover data of YRD and PRD in 2010 (<b>a</b>,<b>b</b>) and 2020 (<b>c</b>,<b>d</b>).</p>
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<p>Workflow diagram.</p>
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<p>Conceptual flowchart of afforestation, reforestation, and deforestation dataset construction algorithm.</p>
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<p>Historical yearly distribution of afforestation (<b>a</b>,<b>d</b>), reforestation (<b>b</b>,<b>e</b>), and deforestation (<b>c</b>,<b>f</b>) in the YRD and PRD from 2010 to 2020, respectively.</p>
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<p>Annual change in the area rate of afforestation, reforestation, and deforestation in the YRD (<b>a</b>) and PRD (<b>b</b>) regions from 2010 to 2020.</p>
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<p>Spatial distribution of effective grids for afforestation (<b>a</b>,<b>b</b>), reforestation (<b>c</b>,<b>d</b>), deforestation (<b>e</b>,<b>f</b>), and conversion of afforestation to non-forests (<b>g</b>,<b>h</b>) in the YRD and PRD regions from 2010 to 2020.</p>
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<p>Seasonal impacts of afforestation (<b>a</b>), reforestation (<b>b</b>), deforestation (<b>c</b>), and conversion of afforestation to non-forests (<b>d</b>) on LST change trend in the YRD and PRD regions from 2010 to 2020, respectively.</p>
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14 pages, 5319 KiB  
Article
Toxicity of Iron Mining Tailings and Potential for Revegetation Using Schinus terebinthifolia Raddi Based on the Emergence, Growth, and Anatomy of the Species
by Poliana Noemia da Silva, Carlos Henrique Goulart dos Reis, Vinícius Politi Duarte, Evaristo Mauro de Castro, Maxwell Pereira de Pádua and Fabricio José Pereira
Mining 2024, 4(3), 719-732; https://doi.org/10.3390/mining4030040 - 23 Sep 2024
Viewed by 450
Abstract
This study aimed to evaluate the emergence, early growth, and anatomy of Schinus terebinthifolia Raddi cultivated in iron mining tailings. The seeds were obtained from trees used in urban afforestation and cultivated on two substrates: sand and iron mining tailings. The chemical composition [...] Read more.
This study aimed to evaluate the emergence, early growth, and anatomy of Schinus terebinthifolia Raddi cultivated in iron mining tailings. The seeds were obtained from trees used in urban afforestation and cultivated on two substrates: sand and iron mining tailings. The chemical composition of the mining tailing was characterized. The experiment was conducted in a growth room for 60 days. The emergence rate, seedling survival, height, number of leaves, chlorophyll content, and leaf and root anatomy were evaluated. The analysis of the composition of the mining tailings indicated that macro- and micronutrients were present, as well as potentially toxic elements such as Al, Cd, Cr, and Pb. The mining tailings reduced the emergence rate, and 25% of the seedlings died in this substrate. In addition, the mining tailings promoted a significant reduction in all parameters investigated, including seedling height, number of leaves, chlorophyll content, total leaf thickness, abaxial and adaxial epidermis thickness, palisade parenchyma thickness, and the length and width of the seeds. Additionally, the chloroplasts, the metaxylem vessel diameter, and the phloem proportion were evaluated. Interestingly, the tailings promoted an increase in the secretory channel. In the roots, no significant changes were observed in the parameters analyzed. Thus, the seeds of S. terebinthifolia germinated in the iron mining tailings, and 75% of the seedlings survived, showing their potential for reforestation. Nonetheless, iron mining tailings exhibited toxicity to S. terebinthifolia seedlings, reducing their photosynthetic tissues and, consequently, their growth; this toxicity is likely related to potentially toxic elements present in tailings. Full article
(This article belongs to the Special Issue Feature Papers in Sustainable Mining Engineering 2024)
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<p>Growth parameters of <span class="html-italic">Schinus terebinthifolia</span> seedlings grown on the following substrates: iron mining tailings and sand. The bars indicate the standard error. For graphs (<b>A</b>–<b>D</b>), the means followed by different letters indicate significant differences according to the Scott–Knott test at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Qualitative effects of iron mining tailings from the Fundão dam failure in Mariana, MG, on <span class="html-italic">Schinus terebinthifolia</span> seedlings. (<b>A</b>) = Seedling emergence; the white arrow indicates the effects caused by the tailings trapping the cotyledons and hindering the vertical growth of the aerial part. The white arrow indicates cotyledons trapped in the substrate. (<b>B</b>) = Inhibition of the growth of the root system of the seedlings that were cultivated in the tailings. (<b>C</b>) = Compound leaves of the seedlings grown for 60 days in sand. (<b>D</b>) = Leaves composed of seedlings grown in tailings for 60 days. The black arrow indicates negative effects on the development of leaves with a lower number of leaflets and deformation of the leaf blade with a change in the edge of the leaflet base [black arrow]. Bars = 2 cm.</p>
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<p>Anatomical characteristics of the interveinal region of <span class="html-italic">Schinus terebinthifolia</span> leaves grown on the following substrates: iron mining tailings and sand. The bars indicate the standard error. For graphs (<b>A</b>,<b>C</b>,<b>E</b>), the means followed by different letters indicate significant differences according to the Scott–Knott test for <span class="html-italic">p</span> &lt; 0.05. For graphs (<b>B</b>,<b>D</b>,<b>F</b>), the means followed by the same letters did not differ significantly according to the Scott–Knott test at <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Leaf anatomy of <span class="html-italic">Schinus terebinthifolia</span> grown on the following substrates: sand (<b>A</b>,<b>C</b>) and iron mining tailings (<b>B</b>,<b>D</b>). Images A and B show the interneural region, and images (<b>C</b>,<b>D</b>) show the midrib. ade = adaxial epidermis; pp = palisade parenchyma; sp = spongy parenchyma; abe = abaxial epidermis; chl = chloroplast; st = stomata; xl = xylem; ph = phloem; sd = secretory channel; vb = vascular bundle, Col = collenchyma; Tr = trichome. Bars = 100 µm.</p>
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<p>Chloroplast characteristics of <span class="html-italic">Schinus terebinthifolia</span> leaves grown on the following substrates: iron mining tailings and sand. The bars indicate the standard error. For graphs (<b>B</b>–<b>D</b>), the means followed by different letters indicate significant changes according to the Scott–Knott test for <span class="html-italic">p</span> &lt; 0.05. For graph (<b>A</b>), the means followed by the same letters did not significantly differ according to the Scott–Knott test for <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Anatomical characteristics of the midrib of <span class="html-italic">Schinus terebinthifolia</span> cultivated on the following substrates: iron mining tailings and sand. The bars indicate the standard error. For graphs (<b>B</b>,<b>C</b>,<b>E</b>), the means followed by different letters indicate significant changes according to the Scott–Knott test for <span class="html-italic">p</span> &lt; 0.05. For graphs (<b>A</b>,<b>D</b>), the means followed by the same letters did not differ significantly according to the Scott–Knott test for <span class="html-italic">p</span> &lt; 0.05.</p>
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<p>Cross-sections of the primary roots of <span class="html-italic">Schinus terebinthifolia</span>. (<b>a</b>) = overview, (<b>b</b>) = cortex and epidermis, (<b>c</b>) = vascular system, (<b>d</b>) = pith. ep = epidermis, ed = endodermis, cs = Caspary band, ca = cambium, ct = cortex, ph = phloem, xl = xylem, pi = pith, cp = cortical parenchyma, is = intercellular space, sd = secretory channel, cr = crystal, ppa = ground parenchyma. Bars = 50 µm (<b>a</b>); 25 µm (<b>b</b>–<b>d</b>).</p>
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27 pages, 5293 KiB  
Article
Dynamic Impact of Digital Inclusive Finance and Financial Market Development on Forests and Timber in China: Economic and Social Perspective
by Rizwana Yasmeen and Guo Hong Fu
Forests 2024, 15(9), 1655; https://doi.org/10.3390/f15091655 - 19 Sep 2024
Viewed by 699
Abstract
This study investigates how digital inclusive finance, financial development, and technology influenced forest and timber outputs across 31 provinces in China from 2011 to 2021. The findings, derived from panel quantile regression analysis, indicate that digital inclusive finance significantly enhances forest economic output, [...] Read more.
This study investigates how digital inclusive finance, financial development, and technology influenced forest and timber outputs across 31 provinces in China from 2011 to 2021. The findings, derived from panel quantile regression analysis, indicate that digital inclusive finance significantly enhances forest economic output, particularly in regions with lower economic activity, by improving access to critical financial resources such as credit and investment. However, the positive effects diminish at higher levels of economic activity, suggesting potential diminishing returns. Through the marketization of credit distribution and diverse financial instruments, financial development is essential for promoting sustainable forestry practices and adopting new technologies. Based on the findings, the study suggests expanding digital financial services in areas with low forest activity to help people access credit and investments, boosting forest productivity. It also recommends improving financial markets and investing in new forestry technologies to support better forest management and timber production. Full article
(This article belongs to the Section Forest Economics, Policy, and Social Science)
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<p>Average forest area of provinces by year (2011–2021).</p>
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<p>Average timber output of provinces by year (2011–2021).</p>
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<p>Average of forestry output growth of the provinces by year (2011–2021).</p>
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<p>Forestry output (100 million) and sum of timber output (10,000 cubic meters) (2011–2021) by province.</p>
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<p>Sum of forest area (10,000 hectares) (2011–2021) by province.</p>
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<p>Assessment road map.</p>
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<p>(<b>a</b>–<b>c</b>) Quantiles for forest output with digital inclusive finance.</p>
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<p>(<b>a</b>–<b>c</b>) Quantiles for forest output with digital inclusive finance.</p>
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<p>(<b>a</b>–<b>c</b>) Quantiles for timber output with digital inclusive finance.</p>
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<p>(<b>a</b>–<b>c</b>) Quantiles for timber output with digital inclusive finance.</p>
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<p>(<b>a</b>,<b>b</b>) Quantiles for forest output with financial development.</p>
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<p>(<b>a</b>,<b>b</b>) Quantiles for forest output with financial development.</p>
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<p>(<b>a</b>,<b>b</b>) Quantiles for timber output with financial development.</p>
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<p>(<b>a</b>,<b>b</b>) Quantiles for timber output with financial development.</p>
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15 pages, 3264 KiB  
Article
Successions of Bacterial and Fungal Communities in Biological Soil Crust under Sand-Fixation Plantation in Horqin Sandy Land, Northeast China
by Chengyou Cao, Ying Zhang and Zhenbo Cui
Forests 2024, 15(9), 1631; https://doi.org/10.3390/f15091631 - 15 Sep 2024
Viewed by 604
Abstract
Biological soil crusts (BSCs) serve important functions in conserving biodiversity and ecological service in arid and semi-arid regions. Afforestation on shifting sand dunes can induce the formation of BSC on topsoil, which can accelerate the restoration of a degraded ecosystem. However, the studies [...] Read more.
Biological soil crusts (BSCs) serve important functions in conserving biodiversity and ecological service in arid and semi-arid regions. Afforestation on shifting sand dunes can induce the formation of BSC on topsoil, which can accelerate the restoration of a degraded ecosystem. However, the studies on microbial community succession along BSC development under sand-fixation plantations in desertification areas are limited. This paper investigated the soil properties, enzymatic activities, and bacterial and fungal community structures across an age sequence (0-, 10-, 22-, and 37-year-old) of BSCs under Caragana microphylla sand-fixation plantations in Horqin Sandy Land, Northeast China. The dynamics in the diversities and structures of soil bacterial and fungal communities were detected via the high-throughput sequencing of the 16S and ITS rRNA genes, respectively. The soil nutrients and enzymatic activities all linearly increased with the development of BSC; furthermore, soil enzymatic activity was more sensitive to BSC development than soil nutrients. The diversities of the bacterial and fungal communities gradually increased along BSC development. There was a significant difference in the structure of the bacterial/fungal communities of the moving sand dune and BSC sites, and similar microbial compositions among different BSC sites were found. The successions of microbial communities in the BSC were characterized as a sequential process consisting of an initial phase of the faster recoveries of dominant taxa, a subsequent slower development phase, and a final stable phase. The quantitative response to BSC development varied with the dominant taxa. The secondary successions of the microbial communities of the BSC were affected by soil factors, and soil moisture, available nutrients, nitrate reductase, and polyphenol oxidase were the main influencing factors. Full article
(This article belongs to the Section Forest Soil)
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<p>Cluster analysis of the structures of soil bacterial (<b>a</b>) and fungal (<b>b</b>) communities. MSD: moving sand dune; SC-10, SC-22, and SC-37: 10-, 22-, and 37-year biological soil crust, respectively.</p>
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<p>Relative abundances of dominant taxa in different sites. (<b>a</b>): bacterial phylum; (<b>b</b>): bacterial genus; (<b>c</b>): fungal phylum; (<b>d</b>): fungal genus. MSD: moving sand dune; SC-10, SC-22, and SC-37: 10-, 22-, and 37-year biological soil crust, respectively.</p>
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<p>Linear responses of the relative abundances of dominant bacterial phyla to biological soil crust age. (<b>a</b>): Proteobacteria; (<b>b</b>): Actinobacteria; (<b>c</b>): Chloroflexi; (<b>d</b>): Bacteroidetes.</p>
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<p>Linear responses of the relative abundances of dominant bacterial genera to BSC age. (<b>a</b>): <span class="html-italic">Sphingomonas</span>; (<b>b</b>): RB41; (<b>c</b>): <span class="html-italic">Ambiguous</span>; (<b>d</b>): <span class="html-italic">Segetibacter</span>; (<b>e</b>): <span class="html-italic">Flavisolibacter</span>; (<b>f</b>): <span class="html-italic">Haliangium</span>; (<b>g</b>): <span class="html-italic">Pseudarthrobacter</span>; (<b>h</b>): <span class="html-italic">Roseiflexus</span>.</p>
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<p>RDA between bacterial (<b>a</b>)/fungal (<b>b</b>) community structure and soil properties. SM: soil moisture; SOM: soil organic matter; TN: total N; AN: NH<sub>4</sub>-N; TP: total P; AP: available P; AK: available K. MSD: moving sand dune (0 yr); SC10, SC22, and SC37: 10, 22, and 37 yr biological soil crust, respectively.</p>
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12 pages, 4519 KiB  
Article
Determination and Analysis of Endogenous Hormones and Cell Wall Composition between the Straight and Twisted Trunk Types of Pinus yunnanensis Franch
by Hailin Li, Rong Xu, Cai Wang, Xiaolin Zhang, Peiling Li, Zhiyang Wu and Dan Zong
Forests 2024, 15(9), 1626; https://doi.org/10.3390/f15091626 - 14 Sep 2024
Viewed by 500
Abstract
Pinus yunnanensis Franch., one of the pioneer species of wild mountain afforestation in southwest China, plays an essential role in the economy, society and environment of Yunnan Province. Nonetheless, P. yunnanensis’ trunk twisting and bending phenomenon has become more common, which significantly [...] Read more.
Pinus yunnanensis Franch., one of the pioneer species of wild mountain afforestation in southwest China, plays an essential role in the economy, society and environment of Yunnan Province. Nonetheless, P. yunnanensis’ trunk twisting and bending phenomenon has become more common, which significantly restricts its use and economic benefits. In order to clarify the compositional differences between the straight and twisted trunk types of P. yunnanensis and to investigate the reasons for the formation of twisted stems, the present study was carried out to dissect the macroscopic and microscopic structure of the straight and twisted trunk types of P. yunnanensis, to determine the content of cell wall components (lignin, cellulose, hemicellulose), determine the content of endogenous hormones, and the expression validation of phytohormone-related differential genes (GA2OX, COI1, COI2) and cell wall-related genes (XTH16, TCH4). The results showed that the annual rings of twisted trunk types were unevenly distributed, eccentric growth, insignificant decomposition of early and late wood, rounding and widening of the tracheid cells, thickening of the cell wall, and reduction of the cavity diameter; the lignin and hemicellulose contents of twisted trunk types were higher; in twisted trunk types, the contents of gibberellin (GA) and jasmonic acid (JA) increased, and the content of auxin (IAA) was reduced; the GA2OX were significantly down-regulated in twisted trunk types, and the expressions of the genes associated with the cell wall, COI1, COI2, TCH4 and XTH16, were significantly up-regulated. In conclusion, the present study found that the uneven distribution of endogenous hormones may be an important factor leading to the formation of twisted trunk type of P. yunnanensis, which adds new discoveries to reveal the mechanism of the genesis of different trunk types in plants, and provides a theoretical basis for the genetic improvement of forest trees. Full article
(This article belongs to the Section Genetics and Molecular Biology)
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<p>Macrostructural observation of straight and twisted <span class="html-italic">P. yunnanensis</span>. (<b>a</b>): Straight type (S), (<b>b</b>): twisted type (T); the arrows point to the eccentricity of the distribution of annual rings from the fifth year onwards.</p>
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<p>Microanatomy of straight and twisted trunk types of <span class="html-italic">P. yunnanensis</span>. Straight trunked type (<b>a</b>–<b>c</b>), twisted trunk type (<b>d</b>–<b>f</b>). Comparison of early and latewood demarcation (<b>a</b>,<b>d</b>); comparison of earlywood (<b>b</b>,<b>e</b>); comparison of latewood (<b>c</b>,<b>f</b>); comparison of average tracheid cell width (<b>g</b>), comparison of cavity diameter size (<b>h</b>), comparison of average double-wall thickness (<b>i</b>). S, straight trunk type; T, twisted trunk type. Double asterisk (**) means extremely significant difference (<span class="html-italic">p</span> &lt; 0.01).</p>
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<p>Differences in lignin (<b>a</b>), hemicellulose (<b>b</b>) and cellulose (<b>c</b>) contents of straight and twisted trunk types of <span class="html-italic">P. yunnanensis</span>. S, straight trunk type; T, twisted trunk type. Double asterisk (**) means extremely significant difference (<span class="html-italic">p</span> &lt; 0.01).</p>
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<p>Differences in endogenous hormone content of straight and twisted trunk types of <span class="html-italic">P. yunnanensis</span>. S, straight trunk type; T, twisted trunk type. Asterisk (*) means significant difference (<span class="html-italic">p</span> &lt; 0.05), and double asterisk (**) means extremely significant difference (<span class="html-italic">p</span> &lt; 0.01). GA<sub>7</sub>: Gibberellin A7; GA<sub>4</sub>: Gibberellin A4; GA<sub>3</sub>: Gibberellin A3;GA<sub>1</sub>: Gibberellin A1; ICA: Indole-3-carboxaldehyde; IBA: 3-Indolebutyric acid; IAA: Indole-3-acetic acid; BR: Brassinolide; TZ: trans-Zeatin; IP: N6-Isopentenyladenine; IPR: isopentenyladenine riboside; SA: Salicylic acid; JA-ILE: Jasmonoyl-L-Isoleucine; JA: Jasmonic acid; H2JA: Dihydrojasmonic acid.</p>
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<p>Differential gene expression of straight and twisted trunk types of <span class="html-italic">P. yunnanensis</span>. S, straight trunk type; T, twisted trunk type. Double asterisk (**) means extremely significant difference (<span class="html-italic">p</span> &lt; 0.01), and three asterisks (***) means extremely significant difference (<span class="html-italic">p</span> &lt; 0.001).</p>
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