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16 pages, 10835 KiB  
Article
Comparative Phylogenomic Study of Malaxidinae (Orchidaceae) Sheds Light on Plastome Evolution and Gene Divergence
by Meng-Yao Zeng, Ming-He Li, Siren Lan, Wei-Lun Yin and Zhong-Jian Liu
Int. J. Mol. Sci. 2024, 25(20), 11181; https://doi.org/10.3390/ijms252011181 - 17 Oct 2024
Abstract
Malaxidinae is one of the most confusing groups in the Orchidaceae classification. Previous phylogenetic analyses have revealed that the relationships between the taxa in Malaxidinae have not yet been reliably established, using only a few plastome regions and nuclear ribosomal internal transcribed spacer [...] Read more.
Malaxidinae is one of the most confusing groups in the Orchidaceae classification. Previous phylogenetic analyses have revealed that the relationships between the taxa in Malaxidinae have not yet been reliably established, using only a few plastome regions and nuclear ribosomal internal transcribed spacer (nrITS). In the present study, the complete plastomes of Oberonia integerrima and Crepidium purpureum were assembled using high-throughput sequencing. Combined with publicly available complete plastome data, this resulted in a dataset of 19 plastomes, including 17 species of Malaxidinae. The plastome features and phylogenetic relationships were compared and analyzed. The results showed the following: (1) Malaxidinae species plastomes possess the quadripartite structure of typical angiosperms, with sizes ranging from 142,996 to 158,787 bp and encoding from 125 to 133 genes. The ndh genes were lost or pseudogenized to varying degrees in six species. An unusual inversion was detected in the large single-copy region (LSC) of Oberonioides microtatantha. (2) Eight regions, including ycf1, matK, rps16, rpl32, ccsA-ndhD, clpP-psbB, trnFGAA-ndhJ, and trnSGCU-trnGUCC, were identified as mutational hotspots. (3) Based on complete plastomes, 68 protein-coding genes, and 51 intergenic regions, respectively, our phylogenetic analyses revealed the genus-level relationships in this subtribe with strong support. The Liparis was supported as non-monophyletic. Full article
(This article belongs to the Special Issue Molecular Research on Orchid Plants)
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Figure 1

Figure 1
<p>Annotation map of the plastomes for <span class="html-italic">Oberonia integerrima</span> (<b>A</b>) and <span class="html-italic">Crepidium purpureum</span> (<b>B</b>).</p>
Full article ">Figure 2
<p>Alignment of 19 Malaxidinae plastomes using Mauve. Comparative gene maps showed an inversion in the <span class="html-italic">rpl33</span>-<span class="html-italic">rps3</span> region of <span class="html-italic">Oberonioides microtatantha</span>. The locally collinear blocks are represented by blocks of the same color connected by lines. Genome regions are color-coded as CDS, tRNA, rRNA, and non-coding region.</p>
Full article ">Figure 3
<p>Comparison of boundaries between the LSC, SSC, and IR regions among 19 Malaxidinae plastomes.</p>
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<p>The RSCU values of 68 concatenated protein-coding genes for Malaxidinae plastomes. Color key: the red values indicate higher RSCU values and the blue values indicate lower RSCU values.</p>
Full article ">Figure 5
<p>mVISTA map of Malaxidinae plastomes with <span class="html-italic">L. bootanensis</span> as reference. The y-axis shows the coordinates between the plastomes.</p>
Full article ">Figure 6
<p>Nucleotide mutation hotspots of protein-coding region (<b>A</b>) and intergenic region (<b>B</b>) of Malaxidinae plastomes. The red and blue points indicate the top four proportion of the variable sites and parsimony information sites, respectively, with the protein-coding region and the intergenic region.</p>
Full article ">Figure 7
<p>Phylogenetic tree of Malaxidinae obtained via maximum likelihood analysis based on 68 protein-coding regions (<b>A</b>) and 51 intergenic regions (<b>B</b>). Numbers near the nodes are bootstrap percentages and Bayesian posterior probabilities (BS<sub>ML</sub>, left; BS<sub>MP</sub>, middle; and PP, right). An asterisk (*) indicates the node has 100% bootstrap or 1.00 posterior probability.</p>
Full article ">Figure 8
<p>Phylogenetic tree of Malaxidinae obtained via maximum likelihood analysis based on whole plastome dataset. Numbers near the nodes are bootstrap percentages and Bayesian posterior probabilities (BS<sub>ML</sub>, left; BS<sub>MP</sub>, middle; and PP, right). An asterisk (*) indicates the node has 100% bootstrap or 1.00 posterior probability. Green represents the terrestrial clade, while orange represents the epiphytic clade. The species names in bold indicate those sequenced in this study.</p>
Full article ">Figure 9
<p>Phylogenetic tree of Malaxidinae obtained via maximum likelihood (ML) analysis based on the top-four protein-coding gene hotspots (<span class="html-italic">ycf1</span>, <span class="html-italic">matK</span>, <span class="html-italic">rps16</span>, and <span class="html-italic">rpl32</span>) (<b>A</b>) and the top-four intergenic region hotspots (<span class="html-italic">ccsA</span>-<span class="html-italic">ndhD</span>, <span class="html-italic">clpP</span>-<span class="html-italic">psbB</span>, <span class="html-italic">trnF<sup>GAA</sup></span>-<span class="html-italic">ndhJ</span>, and <span class="html-italic">trnS<sup>GCU</sup></span>-<span class="html-italic">trnG<sup>UCC</sup></span>) (<b>B</b>). Numbers near the nodes are bootstrap percentages for ML analysis. An asterisk (*) indicates the node has 100% bootstrap probability.</p>
Full article ">
23 pages, 16904 KiB  
Article
Landscape Dynamics, Succession, and Forecasts of Cunninghamia lanceolata in the Central Producing Regions of China
by Zejie Liu, Yongde Zhong, Zhao Chen, Juan Wei, Dali Li and Shuangquan Zhang
Forests 2024, 15(10), 1817; https://doi.org/10.3390/f15101817 - 17 Oct 2024
Abstract
Cunninghamia lanceolata (Lamb.) Hook accounts for 12% of the total forest area in southern China, second only to Masson pine forests, and is an important part of the forest landscape in this region, which has a significant impact on the overall forest structure [...] Read more.
Cunninghamia lanceolata (Lamb.) Hook accounts for 12% of the total forest area in southern China, second only to Masson pine forests, and is an important part of the forest landscape in this region, which has a significant impact on the overall forest structure in southern China. In this study, we used kernel density analysis, landscape index calculation, variance test, and Markov prediction to analyze and forecast the evolution trend of landscape pattern in the central area of C. lanceolata in ten years. The objective is to investigate the change trend of the spatial pattern of C. lanceolata landscape in the long time series and its possible impact on zonal vegetation, as well as the macro-succession trend of C. lanceolata under the current social and economic background, and to make a scientific and reasonable prediction of its future succession trend. The current and future forecast results show that the landscape fragmentation degree of C. lanceolata is intensified, the erosion of bamboo forest is continuously intensified, and the landscape quality is continuously low. These results provide a reference for the future development direction of C. lanceolata and emphasize the need for targeted C. lanceolata management strategies in the future development of C. lanceolata, emphasizing the strengthening of monitoring, controlling harvesting, and managing bamboo competition in order to balance wood production with landscape quality and ecosystem stability. Full article
(This article belongs to the Section Forest Inventory, Modeling and Remote Sensing)
18 pages, 3908 KiB  
Article
Identification of New Cultivar and Different Provenances of Dendrocalamus brandisii (Poaceae: Bambusoideae) Using Simple Sequence Repeats Developed from the Whole Genome
by Ruiman Geng, Junlei Xu, Jutang Jiang, Zhanchao Cheng, Maosheng Sun, Nianhe Xia and Jian Gao
Plants 2024, 13(20), 2910; https://doi.org/10.3390/plants13202910 - 17 Oct 2024
Abstract
Dendrocalamus brandisii is a high-quality bamboo species that can be used for both bamboo shoots and wood. The nutritional components and flavors of D. brandisii vary from different geographical provenances. However, the unique biological characteristics of bamboo make morphological classification methods unsuitable for [...] Read more.
Dendrocalamus brandisii is a high-quality bamboo species that can be used for both bamboo shoots and wood. The nutritional components and flavors of D. brandisii vary from different geographical provenances. However, the unique biological characteristics of bamboo make morphological classification methods unsuitable for distinguishing them. Although the new cultivar ‘Manxie No.1’ has significant differences in the branch characteristics and the color of shoot sheaths compared to the D. brandisii, it still lacks precise genetic information at the molecular level. This study identified 231,789 microsatellite markers based on the whole genome of D. brandisii and analyzed their type composition and distribution on chromosomes in detail. Then, using TP-M13-SSR fluorescence-labeling technology, 34 pairs of polymorphic primers were screened to identify the new cultivar ‘Manxie No.1’ and 11 different geographical provenances of D. brandisii. We also constructed DNA fingerprinting profiles for them. At the same time, we mapped six polymorphic SSRs to the gene of D. brandisii, among which SSR673 was mapped to DhB10G011540, which is related to plant immunity. The specific markers selected in this study can rapidly identify the provenances and the new cultivar of D. brandisii and help explore candidate genes related to some important traits. Full article
(This article belongs to the Special Issue The Genetic Architecture of Bamboo Growth and Development)
Show Figures

Figure 1

Figure 1
<p>The proportion of different types of microsatellites. (<b>A</b>) The number and proportion of different types of microsatellites. The black numbers and corresponding shapes represent the number and proportion of single and composite SSRs in all SSRs. The gray numbers and corresponding shapes represent the number and proportion of different types of perfect SSRs in all perfect SSRs. (<b>B</b>) Trends in the number of perfect SSRs with different repetitive motifs.</p>
Full article ">Figure 2
<p>Changes in the content of 2–6 nt motifs with different repetitions. The horizontal axis represents the number of repetitions of 2–6 nt motifs; the vertical axis represents the proportion of a certain type of motif with a certain number of repetitions.</p>
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<p>Localization of SSR on the <span class="html-italic">Dendrocalamus brandisii</span> chromosome. (<b>A</b>) The proportion of SSRs successfully located on chromosomes. (<b>B</b>) The proportion of SSR on 70 chromosomes. The right side of the two orange arrows represents the number of SSRs on DbrChrA01–A35 in a clockwise direction, while the left side of the two orange arrows represents the number of SSRs on DbrChrB01–B35 in a clockwise direction. (<b>C</b>) Localization of SSRs on the 5’UTR, 3’UTR, exon, intron, intergenic, and multi-mapped <span class="html-italic">D. brandisii</span>. (<b>D</b>) The distribution of SSR on 70 chromosomes of <span class="html-italic">D. brandisii</span>.</p>
Full article ">Figure 4
<p>Diagram of cis-acting elements in the promoters of <span class="html-italic">DhB21G011140</span>, <span class="html-italic">DhB31G002880</span>, <span class="html-italic">DhB31G019250</span>, <span class="html-italic">DhA19G015160</span>, <span class="html-italic">DhA19G013950</span>, and <span class="html-italic">DhB10G011540</span>.</p>
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<p>Cluster analysis of 12 materials based on SSR markers. * represents Cangyuan County, Lincang City, Yunnan Province, China, and ** represents Linxiang District, Lincang City, Yunnan Province, China.</p>
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<p>DNA fingerprinting of 12 materials constructed based on 34 pairs of SSR primers. On the right side of the image is the information of 12 materials, with the SSR name above. The number below the image represents the size of all fragments that the corresponding SSR can amplify. Blue and gray, respectively, represent the presence or absence of fragments. * represents Cangyuan County, Lincang City, Yunnan Province, China, and ** represents Linxiang District, Lincang City, Yunnan Province, China.</p>
Full article ">Figure 7
<p>Sampling site labeling diagram for 11 samples of <span class="html-italic">D. brandisii</span> and 1 sample of ‘Manxie No.1’. The figure above shows the location of the sampling sites on a world map. In the figure below, green, red, blue, and purple represent the sampling sites in Yunnan Province, China; Guangdong Province, China; Yenbai Province, Vietnam; and Chiang Mai Province, Thailand.</p>
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17 pages, 5594 KiB  
Article
The Effects of swnH1 Gene Function of Endophytic Fungus Alternaria oxytropis OW 7.8 on Its Swainsonine Biosynthesis
by Dan Li, Xinlei Zhao, Ping Lu and Yu Min
Microorganisms 2024, 12(10), 2081; https://doi.org/10.3390/microorganisms12102081 - 17 Oct 2024
Abstract
The swnH1 gene in the endophytic fungus Alternaria oxytropis OW 7.8 isolated from Oxytropis glabra was identified, and the gene knockout mutant ΔswnH1 was first constructed in this study. Compared with A. oxytropis OW 7.8, the ΔswnH1 mutant exhibited altered colony [...] Read more.
The swnH1 gene in the endophytic fungus Alternaria oxytropis OW 7.8 isolated from Oxytropis glabra was identified, and the gene knockout mutant ΔswnH1 was first constructed in this study. Compared with A. oxytropis OW 7.8, the ΔswnH1 mutant exhibited altered colony and mycelium morphology, slower growth rate, and no swainsonine (SW) in mycelia, indicating that the function of the swnH1 gene promoted SW biosynthesis. Five differential expressed genes (DEGs) closely associated with SW synthesis were identified by transcriptomic analysis of A. oxytropis OW 7.8 and ΔswnH1, with sac, swnR, swnK, swnN, and swnH2 down-regulating. Six differential metabolites (DEMs) closely associated with SW synthesis were identified by metabolomic analysis, with P450, PKS-NRPS, saccharopine, lipopolysaccharide kinase, L-PA, α-aminoadipic, and L-stachydrine down-regulated, while L-proline was up-regulated. The SW biosynthetic pathways in A. oxytropis OW 7.8 were predicted and refined. The results lay the foundation for in-depth exploration of the molecular mechanisms and metabolic pathways of SW synthesis in fungi and provide reference for future control of SW in locoweeds, which would benefit the development of animal husbandry and the sustainable use of grassland ecosystems. Full article
(This article belongs to the Section Molecular Microbiology and Immunology)
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Figure 1

Figure 1
<p>SW biosynthetic pathways in two fungi. (<b>A</b>) <span class="html-italic">R. leguminicola</span> and (<b>B</b>) <span class="html-italic">M. robertsii</span> [<a href="#B27-microorganisms-12-02081" class="html-bibr">27</a>,<a href="#B38-microorganisms-12-02081" class="html-bibr">38</a>].</p>
Full article ">Figure 2
<p>Diagram of the <span class="html-italic">swnH1</span> gene knockout vector structure. Amp: Ampicillin; Ori: Origin of replication; <span class="html-italic">swnH1</span> up: the upstream homologous sequences of <span class="html-italic">swnH1</span>; <span class="html-italic">swnH1</span> down: the downstream homologous sequences of <span class="html-italic">swnH1</span>; <span class="html-italic">hpt</span>: hygromycin phosphotransferase gene; <span class="html-italic">lacZ</span>: <span class="html-italic">lacZ</span> gene.</p>
Full article ">Figure 3
<p>Identification figure for <span class="html-italic">swnH1</span> gene knockout transformants.</p>
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<p>Bioinformatics analysis of the <span class="html-italic">swnH1</span> gene. (<b>A</b>) Predicted SwnH1 protein structure; (<b>B</b>) the phylogenetic tree of the SwnH1 protein.</p>
Full article ">Figure 5
<p>Colonies of <span class="html-italic">A. oxytropis</span> OW 7.8 on PDA media containing different concentrations of Hyg B after 30 days of incubation. (<b>A</b>) 0 μg/mL. (<b>B</b>) 0.4 μg/mL. (<b>C</b>) 0.5 μg/mL. (<b>D</b>) 0.6 μg/mL. (<b>E</b>) 0.7 μg/mL. (<b>F</b>) 0.8 μg/mL. (<b>G</b>) 0.9 μg/mL. (<b>H</b>) 1.0 μg/mL. (<b>I</b>) 2.0 μg/mL. (<b>J</b>) 3.0 μg/mL.</p>
Full article ">Figure 6
<p>Electrophoresis analysis of PCR products of transformant DNA. Marker: 1 kb plus DNA ladder. (<b>A</b>) Lanes 1, 2, 3 show bands of the <span class="html-italic">hpt</span> gene, with the expected product being 1388 bp; W: negative control. (<b>B</b>) Lanes 1, 2, 3 show bands of the <span class="html-italic">hpt</span> gene + downstream homologous sequence of the <span class="html-italic">swnH1</span>, with the expected product being 1703 bp; W: negative control. (<b>C</b>) Lanes 1, 2 show bands of the upstream homologous sequence of <span class="html-italic">swnH1</span> + <span class="html-italic">hpt</span> gene, with the expected product being 1998 bp; W: negative control. (<b>D</b>) Lanes 1, 2, 3 show unamplified internal sequence of <span class="html-italic">swnH1</span>; W: positive control, with the expected product being 987 bp.</p>
Full article ">Figure 7
<p>Morphology of colonies and mycelia from <span class="html-italic">A. oxytropis</span> OW 7.8 and Δ<span class="html-italic">swnH1.</span> (<b>A</b>) <span class="html-italic">A. oxytropis</span> OW 7.8 colonies. (<b>B</b>) Δ<span class="html-italic">swnH1</span> colonies. (<b>C</b>) <span class="html-italic">A. oxytropis</span> OW 7.8 mycelia magnified 3000×. (<b>D</b>) Δ<span class="html-italic">swnH1</span> mycelia magnified 3000×.</p>
Full article ">Figure 8
<p>SW levels in mycelia from <span class="html-italic">A. oxytropis</span> OW 7.8 and Δ<span class="html-italic">swnH1</span>. Error bars represent the standard error of the mean (<span class="html-italic">n</span> = 3), with (****) <span class="html-italic">p</span> &lt; 0.0001.</p>
Full article ">Figure 9
<p>Transcriptome analysis between <span class="html-italic">A. oxytropis</span> OW 7.8 and Δ<span class="html-italic">swnH1</span>. (<b>A</b>) Volcano plot for differential comparison. (<b>B</b>) KEGG enrichment analysis and (<b>C</b>) GO functional classification annotation. BP: Biological Process; CC: Cellular Component; MF: Molecular Function.</p>
Full article ">Figure 10
<p>Metabolome analysis between <span class="html-italic">A. oxytropis</span> OW 7.8 and Δ<span class="html-italic">swnH1</span>. (<b>A</b>) Principal component analysis in positive ion mode. (<b>B</b>) Principal component analysis in negative ion mode. (<b>C</b>) Pie chart of metabolite classification in positive ion mode. (<b>D</b>) Pie chart of metabolite classification in negative ion mode. (<b>E</b>) differential metabolite volcano plot in positive ion mode. (<b>F</b>) differential metabolite volcano plot in negative ion mode. (<b>G</b>) Scatter plot of KEGG enrichment of differential metabolites in positive ion mode. (<b>H</b>) Scatter plot of KEGG enrichment of differential metabolites in negative ion mode. (<b>I</b>) KEGG enrichment analysis of DEMs.</p>
Full article ">Figure 10 Cont.
<p>Metabolome analysis between <span class="html-italic">A. oxytropis</span> OW 7.8 and Δ<span class="html-italic">swnH1</span>. (<b>A</b>) Principal component analysis in positive ion mode. (<b>B</b>) Principal component analysis in negative ion mode. (<b>C</b>) Pie chart of metabolite classification in positive ion mode. (<b>D</b>) Pie chart of metabolite classification in negative ion mode. (<b>E</b>) differential metabolite volcano plot in positive ion mode. (<b>F</b>) differential metabolite volcano plot in negative ion mode. (<b>G</b>) Scatter plot of KEGG enrichment of differential metabolites in positive ion mode. (<b>H</b>) Scatter plot of KEGG enrichment of differential metabolites in negative ion mode. (<b>I</b>) KEGG enrichment analysis of DEMs.</p>
Full article ">Figure 11
<p>SW Biosynthesis Pathway in <span class="html-italic">A. oxytropis</span> OW 7.8. Note: LysX, LysZ, LysY, LysJ, and LysK are trypsin enzymes that can specifically cleave peptide bonds at different positions of lysine. SDH, LYS1, and LYS9 are saccharine reductases. lhpD/dpkA: Delta-1-piperideine-2-carboxylate reductase, lhpI: 1-piperideine-2-carboxylate reductase, PIPOX: <span class="html-italic">L</span>-PA oxidase.</p>
Full article ">
15 pages, 11544 KiB  
Article
Environmental Heat Stress Decreases Sperm Motility by Disrupting the Diurnal Rhythms of Rumen Microbes and Metabolites in Hu Rams
by Qiang-Jun Wang, Huan-Ming Yi, Jing-Yu Ou, Ru Wang, Ming-Ming Wang, Peng-Hui Wang, Xiao-Long He, Wen-Hui Tang, Jia-Hong Chen, Yang Yu, Chun-Ping Zhang, Chun-Huan Ren and Zi-Jun Zhang
Int. J. Mol. Sci. 2024, 25(20), 11161; https://doi.org/10.3390/ijms252011161 - 17 Oct 2024
Abstract
Heat stress (HS) has become a common stressor, owing to the increasing frequency of extreme high-temperature weather triggered by global warming, which has seriously affected the reproductive capacity of important livestock such as sheep. However, little is known about whether HS reduces sperm [...] Read more.
Heat stress (HS) has become a common stressor, owing to the increasing frequency of extreme high-temperature weather triggered by global warming, which has seriously affected the reproductive capacity of important livestock such as sheep. However, little is known about whether HS reduces sperm motility by inducing circadian rhythm disorders in rumen microorganisms and metabolites in sheep. In this study, the year-round reproduction of two-year-old Hu rams was selected, and the samples were collected in May and July 2022 at average environmental temperatures between 18.71 °C and 33.58 °C, respectively. The experiment revealed that the mean temperature-humidity index was 86.34 in July, indicating that Hu rams suffered from HS. Our research revealed that HS significantly decreased sperm motility in Hu rams. Microbiome analysis further revealed that HS reshaped the composition and circadian rhythm of rumen microorganisms, leading to the circadian disruption of microorganisms that drive cortisol and testosterone synthesis. Serum indicators further confirmed that HS significantly increased the concentrations of cortisol during the daytime and decreased the testosterone concentration at the highest body temperature. Untargeted metabolomics analysis revealed that the circadian rhythm of rumen fluid metabolites in the HS group was enriched by the cortisol and steroid synthesis pathways. Moreover, HS downregulated metabolites, such as kaempferol and L-tryptophan in rumen fluid and seminal plasma, which are associated with promotion of spermatogenesis and sperm motility; furthermore, these metabolites were found to be strongly positively correlated with Veillonellaceae_UCG_001. Overall, this study revealed the relationship between the HS-induced circadian rhythm disruption of rumen microorganisms and metabolites and sperm motility decline. Our findings provide a new perspective for further interventions in enhancing sheep sperm motility with regard to the circadian time scale. Full article
(This article belongs to the Section Molecular Microbiology)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Heat stress alters the body temperature, biochemical indexes, and sperm motility in rams. (<b>A</b>–<b>H</b>) The diurnal rhythms based on a Jonckheere–Terpstra–Kendall (JTK) analysis of THI, body temperature, and biochemical indexes <span class="html-italic">(n</span> = 6 per time point). ADJ.P for adjusted minimal <span class="html-italic">p</span>-values, ADJ.P &lt; 0.05, indicates a significant effect on circadian rhythm, AMP represents amplitude, and ZT represents Zeitgeber time. White bars in the graph represent daytime, and gray bars represent nighttime. (<b>I</b>) Sperm motility parameters (<span class="html-italic">n</span> = 6). Asterisks indicate significance at <span class="html-italic">p</span> &lt; 0.05 (*), <span class="html-italic">p</span> &lt; 0.01 (**), <span class="html-italic">p</span> &lt; 0.001 (***).</p>
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<p>Heat stress alters the circadian rhythm of rumen microbes in rams. (<b>A</b>,<b>B</b>) Heat map showing oscillating ASVs in the NH (<b>left</b>) or HS (<b>right</b>) groups. (<b>C</b>,<b>D</b>) The diurnal rhythm of rumen microbes at phylum and genus levels (n = 6 per time point), respectively. (<b>E</b>) The polar plots represent the time when the ASV’s peak level of abundance occurred; blue (NH group) or red (HS group) shading represents the number of rhythmic ASVs with an estimated peak value for each time, as determined with JTK analysis. The radius of black concentric circles indicates the number of rhythmic ASVs, and the minimum radius of the black concentric circle represents one ASV. The black arc on the left side of the polar plot indicates the day/night cycle.</p>
Full article ">Figure 3
<p>Heat stress alters the diurnal pattern of rumen metabolites in rams. (<b>A</b>) Identification of distinct temporal patterns of metabolites in the NH and HS groups using fuzzy c-means clustering. The y-axis represents normalized data based on all metabolites within each cluster. (<b>B</b>) Classification of metabolites. (<b>C</b>) KEGG analysis (<span class="html-italic">p</span> &lt; 0.05) of the metabolites within each cluster in the NH and HS groups.</p>
Full article ">Figure 4
<p>Heat stress alters the circadian rhythm of rumen metabolites in rams. (<b>A</b>) Venn diagram showing the number of rhythmic metabolites and also significant differences between groups. (<b>B</b>) Heat map showing oscillating metabolites in the NH (<b>left</b>) or HS (<b>right</b>) groups. (<b>C</b>) Classification of metabolites. (<b>D</b>) Identification of distinct temporal patterns of metabolites in the NH and HS groups by fuzzy c-means clustering. (<b>E</b>,<b>F</b>) Pathways annotated for rumen metabolites based on the KEGG database (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 5
<p>Heat stress alters the composition of metabolites in rumen fluid and seminal plasma. (<b>A</b>,<b>B</b>) Heat stress altered rumen and seminal plasma metabolomic profiles based on orthogonal partial least-squares discriminant analysis (OPLS-DA) in the NH and HS groups, respectively. Differentially abundant rumen and seminal plasma metabolites were visualized using volcano plots in the NH and HS groups, respectively. (<b>C</b>) Venn diagram showing the number of metabolites between rumen and seminal plasma. (<b>D</b>) Common differential metabolite in rumen fluid and seminal plasma. (<b>E</b>,<b>F</b>) Pathways annotated for rumen fluid and seminal plasma metabolites based on the KEGG database (<span class="html-italic">p</span> &lt; 0.05). Asterisks indicate significance at <span class="html-italic">p</span> &lt; 0.05 (*), <span class="html-italic">p</span> &lt; 0.01 (**).</p>
Full article ">Figure 6
<p>HS altered sperm motility and was related to the diurnal rhythms of rumen microbes and metabolites in rams. (<b>A</b>) Circos plot showing variable correlations among microbiome, metabolome, sperm motility parameters, and biochemical indexes. (<b>B</b>) Sankey diagram illustrating the complex interactions between microbiome, metabolome, and other indicators’ complex interactions. (<b>C</b>,<b>D</b>) Spearman correlation between microbiome, metabolome, sperm motility, and THI (r &gt; 0.5, <span class="html-italic">p</span> &lt; 0.05). Asterisks indicate significance at <span class="html-italic">p</span> &lt; 0.05 (*), <span class="html-italic">p</span> &lt; 0.01 (**).</p>
Full article ">
19 pages, 13917 KiB  
Article
TCSNet: A New Individual Tree Crown Segmentation Network from Unmanned Aerial Vehicle Images
by Yue Chi, Chenxi Wang, Zhulin Chen and Sheng Xu
Forests 2024, 15(10), 1814; https://doi.org/10.3390/f15101814 - 17 Oct 2024
Abstract
As the main area for photosynthesis in trees, the canopy absorbs a large amount of carbon dioxide and plays an irreplaceable role in regulating the carbon cycle in the atmosphere and mitigating climate change. Therefore, monitoring the growth of the canopy is crucial. [...] Read more.
As the main area for photosynthesis in trees, the canopy absorbs a large amount of carbon dioxide and plays an irreplaceable role in regulating the carbon cycle in the atmosphere and mitigating climate change. Therefore, monitoring the growth of the canopy is crucial. However, traditional field investigation methods are often limited by time-consuming and labor-intensive methods, as well as limitations in coverage, which may result in incomplete and inaccurate assessments. In response to the challenges encountered in the application of tree crown segmentation algorithms, such as adhesion between individual tree crowns and insufficient generalization ability of the algorithm, this study proposes an improved algorithm based on Mask R-CNN (Mask Region-based Convolutional Neural Network), which identifies irregular edges of tree crowns in RGB images obtained from drones. Firstly, it optimizes the backbone network by improving it to ResNeXt and embedding the SENet (Squeeze-and-Excitation Networks) module to enhance the model’s feature extraction capability. Secondly, the BiFPN-CBAM module is introduced to enable the model to learn and utilize features more effectively. Finally, it optimizes the mask loss function to the Boundary-Dice loss function to further improve the tree crown segmentation effect. In this study, TCSNet also incorporated the concept of panoptic segmentation, achieving the coherent and consistent segmentation of tree crowns throughout the entire scene through fine tree crown boundary recognition and integration. TCSNet was tested on three datasets with different geographical environments and forest types, namely artificial forests, natural forests, and urban forests, with artificial forests performing the best. Compared with the original algorithm, on the artificial forest dataset, the precision increased by 6.6%, the recall rate increased by 1.8%, and the F1-score increased by 4.2%, highlighting its potential and robustness in tree detection and segmentation. Full article
(This article belongs to the Special Issue Panoptic Segmentation of Tree Scenes from Mobile LiDAR Data)
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<p>The proposed TCSNet structure.</p>
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<p>SE-ResNeXt structure.</p>
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<p>BiFPN and BiFPN-CBAM.</p>
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<p>Urban forest scene. The research area is located near Xuanwu Lake in Nanjing, Jiangsu Province, China. The forest type is mixed forest, and common tree species include camphor (<span class="html-italic">Camphora officinarum</span> Nees ex Wall), ginkgo (<span class="html-italic">Ginkgo biloba</span> L.), pine (<span class="html-italic">Pinus</span> L.), and willow (<span class="html-italic">Salix</span>).</p>
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<p>Artificial forest scene. The research area of the artificial forest dataset is located in Jiangsu Huanghai Haibin National Forest Park in Yancheng. Here, there are vast artificial ecological forests with extremely high forest coverage. Common tree species in the park include metasequoia (<span class="html-italic">Metasequoia glyptostroboides</span> Hu et Cheng) and poplar (<span class="html-italic">Populus</span> spp.).</p>
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<p>UAV image collection equipment: M350RTK.</p>
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<p>Data augmentation of poplar (<span class="html-italic">Populus</span> spp.) trees in artificial forest datasets. (<b>a</b>) Original image; (<b>b</b>) the image is obtained by rotation; (<b>c</b>) the image is obtained by changing the contrast; (<b>d</b>) the image is obtained by changing the saturation.</p>
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<p>Data augmentation of poplar (<span class="html-italic">Populus</span> spp.) trees in artificial forest datasets. (<b>a</b>) Original image; (<b>b</b>) the image is obtained by rotation; (<b>c</b>) the image is obtained by changing the contrast; (<b>d</b>) the image is obtained by changing the saturation.</p>
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<p>Total loss. The total loss considers the training effect of multiple loss function comprehensive indicators.</p>
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<p>Classification loss. The classification loss focuses on evaluating the loss function of model prediction accuracy in classification tasks.</p>
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<p>Loss for bounding box regression. The loss for bounding box regression is used to measure the prediction error of bounding box regression in tree crown detection.</p>
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<p>Segmentation performance of each dataset. (<b>a</b>,<b>b</b>) and (<b>c</b>,<b>d</b>) respectively demonstrate the segmentation performance of TCSNet on two tree species. (<b>e</b>–<b>h</b>) demonstrate the segmentation performance of TCSNet in urban parks and green spaces. (<b>i</b>–<b>l</b>) demonstrated the segmentation performance of TCSNet in tropical rainforests.</p>
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<p>Differences in different datasets. Blue squares represent tree crowns that are difficult to segment. (<b>a</b>,<b>b</b>) Both belong to artificial forests, but (<b>a</b>) has a similar canopy size and a more orderly arrangement, so the segmentation effect is better. (<b>b</b>) More affected by grass, and the crown is irregular, the effect is average. (<b>c</b>) The canopy size is similar, some ordered and some disorderly, but it will still be affected by the shadow, and the segmentation effect is general. (<b>d</b>) The trees are natural forests with small gaps and inconsistent canopy sizes, so segmentation is the most difficult.</p>
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<p>Comparisons with other algorithms [<a href="#B29-forests-15-01814" class="html-bibr">29</a>,<a href="#B30-forests-15-01814" class="html-bibr">30</a>,<a href="#B31-forests-15-01814" class="html-bibr">31</a>]. We achieved most tree crown instances from input data.</p>
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23 pages, 37649 KiB  
Article
Research on Forage–Livestock Balance in the Three-River-Source Region Based on Improved CASA Model
by Chenlu Hu, Yichen Tian, Kai Yin, Huiping Huang, Liping Li and Qiang Chen
Remote Sens. 2024, 16(20), 3857; https://doi.org/10.3390/rs16203857 - 17 Oct 2024
Abstract
As an important ecological barrier and a crucial base for animal husbandry in China, the forage–livestock balance in the Three-River-Source Region (TRSR) directly impacts both the degradation and recovery of grassland. This study examines the forage–livestock balance in the TRSR over the past [...] Read more.
As an important ecological barrier and a crucial base for animal husbandry in China, the forage–livestock balance in the Three-River-Source Region (TRSR) directly impacts both the degradation and recovery of grassland. This study examines the forage–livestock balance in the TRSR over the past 13 years (2010–2022) by calculating both the theoretical and actual livestock carrying capacity, thereby providing a scientific basis for regional animal husbandry policies. Firstly, the Carnegie–Ames–Stanford Approach (CASA) model was improved to fit the specific characteristics of alpine grassland ecosystem in the TRSR. This enhanced model was subsequently used to calculate the net primary productivity (NPP) of the grassland, from which the regional grassland yield and theoretical livestock carrying capacity were derived. Secondly, the actual livestock carrying capacity was calculated and spatialized based on the number of regional year-end livestock. Finally, the livestock carrying pressure index was determined using both the theoretical and actual livestock carrying capacity. The results revealed several key findings: (1) The average grassland NPP in the TRSR was 145.44 gC/m2, the average grassland yield was 922.7 kg/hm2, and the average theoretical livestock carrying capacity was 0.55 SU/hm2 from 2010 to 2022. Notably, all three metrics showed an increasing trend over the past 13 years, which indicates the rise in grassland vegetation activities. (2) The average actual livestock carrying capacity over the 13-year period was 0.46 SU/hm2, showing a decreasing trend on the whole. The spatial distribution displayed a pattern of higher capacity in the east and lower in the west. (3) Throughout the 13 years, the TRSR generally maintained a forage–livestock balance, with an average livestock carrying pressure index of 0.96 (insufficient). However, the trend of livestock carrying pressure is on the rise, with serious overloading observed in the western part of Qumalai County and the northern part of Tongde County. Slight overloading was also noted in Zhiduo, Maduo, and Zeku Counties. Notably, Tanggulashan Town, Zhiduo, Qumalai, and Maduo Counties showed significant increases in livestock carrying pressure, while Zaduo County and the eastern regions experienced significant decreases. In conclusion, this study not only provides feasible technical methods for assessing and managing the forage–livestock balance in the TRSR but also contributes significantly to the sustainable development of the region’s grassland ecosystem and animal husbandry industry. Full article
(This article belongs to the Special Issue Remote Sensing of Mountain and Plateau Vegetation)
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<p>The Three–River–Source Region: (<b>a</b>) digital elevation model and location; (<b>b</b>) grassland vegetation types.</p>
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<p>The spatiotemporal patterns of grassland NPP in the TRSR from 2010 to 2022: (<b>a</b>) mean annual NPP: the inset chart shows the interannual dynamics of NPP from 2010 to 2022, where the red dashed line shows the overall trend of NPP; (<b>b</b>) change trend of NPP: the inset chart shows the area proportion of each; (<b>c</b>) radial accumulation bar chart of NPP in different grassland vegetation types from 2010 to 2022.</p>
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<p>The spatiotemporal patterns of grassland NPP in the TRSR from 2010 to 2022: (<b>a</b>) mean annual NPP: the inset chart shows the interannual dynamics of NPP from 2010 to 2022, where the red dashed line shows the overall trend of NPP; (<b>b</b>) change trend of NPP: the inset chart shows the area proportion of each; (<b>c</b>) radial accumulation bar chart of NPP in different grassland vegetation types from 2010 to 2022.</p>
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<p>The spatiotemporal patterns of grassland yield and theoretical livestock carrying capacity in the TRSR from 2010 to 2022: (<b>a</b>) mean annual grassland yield: the inset chart shows the interannual dynamics of grassland yield from 2010 to 2022, where the red dashed line shows the overall trend of grassland yield; (<b>b</b>) change trend of grassland yield: the inset chart shows the area proportion of each; (<b>c</b>) mean annual theoretical livestock carrying capacity: the inset chart shows the interannual dynamics of theoretical livestock carrying capacity from 2010 to 2022, where the red dashed line shows the overall trend of theoretical livestock carrying capacity; (<b>d</b>) change trend of theoretical livestock carrying capacity: the inset chart shows the area proportion of each.</p>
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<p>Validations of simulated NPP and grassland yield by improved CASA model: (<b>a</b>) the correlation of simulated NPP by improved CASA model and MOD17A3 NPP, where the solid black line represents the fitting curve of simulated NPP and MOD17A3 NPP; (<b>b</b>) the correlation of simulated grassland yield by improved CASA model and observed grassland yield, where the solid black line represents the fitting curve of simulated grassland yield and observed grassland yield.</p>
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<p>The spatiotemporal patterns of actual livestock carrying capacity in the TRSR from 2010 to 2022: (<b>a</b>) mean annual actual livestock carrying capacity: the inset chart shows the interannual dynamics of actual livestock carrying capacity from 2010 to 2022, where the red dashed line shows the overall trend of actual livestock carrying capacity; (<b>b</b>) change trend of actual livestock carrying capacity: the inset chart shows the area proportion of each.</p>
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<p>The spatiotemporal patterns of the livestock carrying pressure in the TRSR from 2010 to 2022: (<b>a</b>) mean annual livestock carrying pressure: the inset chart shows the interannual dynamics of livestock carrying pressure from 2010 to 2022, where the red dashed line shows the overall trend of livestock carrying pressure; (<b>b</b>) change trend of livestock carrying pressure: the inset chart shows the area proportion of each.</p>
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<p>The spatiotemporal patterns of the livestock carrying pressure in the TRSR from 2010 to 2022: (<b>a</b>) mean annual livestock carrying pressure: the inset chart shows the interannual dynamics of livestock carrying pressure from 2010 to 2022, where the red dashed line shows the overall trend of livestock carrying pressure; (<b>b</b>) change trend of livestock carrying pressure: the inset chart shows the area proportion of each.</p>
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<p>Simulated NPP by improved CASA model and unimproved CASA model compared to MOD17A3 NPP product: (<b>a</b>) scatter plot with MOD17A3 NPP; (<b>b</b>) change curve of NPP from 2010 to 2022; (<b>c</b>) histogram of NPP in different grassland vegetation types; (<b>d</b>) radar map of NPP with different elevation grades.</p>
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<p>Livestock carrying pressure in the TRSR from 2010 to 2022: (<b>a</b>) heat map of livestock carrying pressure in each county from 2010 to 2022; (<b>b</b>) changes and average values of livestock carrying pressure in each county for 13 years.</p>
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<p>The spatial distributions of grazing condition and Three–River–Source Nature Reserve (<a href="https://sthjt.qinghai.gov.cn" target="_blank">https://sthjt.qinghai.gov.cn</a>, accessed on 14 July 2024) from 2010 to 2022: (<b>a</b>) mean annual actual livestock carrying capacity; (<b>b</b>) mean annual livestock carrying pressure; (<b>c</b>) mean annual NDVI.</p>
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17 pages, 13560 KiB  
Article
Genome-Wide Characterization of the GRAS Gene Family in Cyclocarya paliurus and Its Involvement in Heterodichogamy
by Qian Wang, Yibo Yang, Yanhao Yu, Di Mei, Xia Mao and Xiangxiang Fu
Agronomy 2024, 14(10), 2397; https://doi.org/10.3390/agronomy14102397 - 17 Oct 2024
Viewed by 65
Abstract
The GRAS gene family, derived from GAI, RGA, and SCR, plays a crucial role in plant growth and development. In the diploid Cyclocarya paliurus (2n = 2x = 32) with heterodichogamous characteristics, 51 CpGRAS genes were identified and phylogenetically classified into 10 subfamilies. [...] Read more.
The GRAS gene family, derived from GAI, RGA, and SCR, plays a crucial role in plant growth and development. In the diploid Cyclocarya paliurus (2n = 2x = 32) with heterodichogamous characteristics, 51 CpGRAS genes were identified and phylogenetically classified into 10 subfamilies. Structural analysis revealed that CpGRAS genes possessed a canonical GRAS domain, but 70% lacked introns. WGD/segmental duplication was the major driver in the expansion of the CpGRAS family. In addition, a Ka/Ks ratio below 1 for these genes implied functional constraints and evolutionary conservation. Transcriptional profiling revealed significant differential expressions of CpGRAS genes between male and female flowers from two mating types, protogyny (PG) and protandry (PA). Notably, members of the DELLA subfamily exhibited significant upregulation in female flowers at the inflorescence elongation (S3) stage. The expression level of CpSCL6-2 in late-flowering samples (PA-F and PG-M) was higher than in early-flowering ones (PA-M and PG-F). Co-expression analysis identified that CpRGL1 and CpGAI-2 of the DELLA subfamily, along with CpSCL6-2, acted as hub genes, implying their crucial roles in floral development and potential involvement in the heterodichogamous flowering mechanism in C. paliurus. These findings broaden our understanding of CpGRAS genes and provide new insights into the molecular basis of heterodichogamy. Full article
(This article belongs to the Section Plant-Crop Biology and Biochemistry)
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<p>Distributions of CpGRAS genes along chromosomes of <span class="html-italic">C. paliurus</span>.</p>
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<p>Phylogenetic analysis of CpGRAS proteins and GRAS proteins obtained from <span class="html-italic">Arabidopsis thaliana</span> and <span class="html-italic">Juglans regia</span>. The arcs in different colors indicate different subfamilies of GRAS.</p>
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<p>Phylogenetic relationships, conserved motifs, and gene structures of GRAS gene family in <span class="html-italic">C. paliurus</span>. (<b>A</b>) The phylogenetic tree was constructed based on the full-length sequences of CpGRAS proteins by MEGA 11. (<b>B</b>) Motif patterns of CpGRAS proteins were depicted with 20 different colored boxes to represent the positions of different motifs. (<b>C</b>) Gene structure was illustrated with exons represented as yellow boxes, introns as thin black lines, and UTRs as green boxes.</p>
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<p>Cis-action elements in the promoter region of CpGRAS genes. (<b>A</b>) Numbers of CREs shown in the promoter region (2000 bp); the greener the color, the greater the number. (<b>B</b>) The distribution of different CREs in the promoter region of CpGRAS genes; different colored boxes represent different CREs.</p>
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<p>Schematic representations for the intrachromosomal relationships of CpGRAS genes. Gray lines indicate all synteny blocks in the <span class="html-italic">C. paliurus</span> genome, and red lines indicate duplicated GRAS gene pairs.</p>
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<p>Synteny analysis of GRAS genes between <span class="html-italic">C. paliurus</span> and other plants. Gray lines in the background indicate the collinear blocks within the genomes of <span class="html-italic">C. paliurus</span> as well as <span class="html-italic">A. thaliana</span> and <span class="html-italic">Vitis vinifera</span>, while the blue lines highlight the syntenic GRAS gene pairs.</p>
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<p>Spatial and temporal expression patterns of CpGRAS genes in <span class="html-italic">C. paliurus</span>. (<b>A</b>) Morphological changes during flower development in <span class="html-italic">C. paliurus</span> [<a href="#B22-agronomy-14-02397" class="html-bibr">22</a>]. S1, dormant stage; S2, bud break stage; S3, inflorescence elongation stage; S4, mature stage. (<b>B</b>) Heat map of CpGRAS genes expression abundance of different tissues. The scales in blue and red indicate low and high transcript expression, respectively. PA-F, female floral buds from protandry; PA-M, male floral buds from protandry; PG-F, female floral buds from protogyny; PG-M, male floral buds from protogyny.</p>
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<p>qRT-PCR validation of candidate genes in different flower buds of <span class="html-italic">C. paliurus</span>. The polyline represents FPKM values in transcriptome data, and the vertical bars shown in the columns represent relative expression levels by qRT-PCR.</p>
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<p>Co-expression networks of CpGRAS genes. The weights between genes are indicated by the thickness of the connecting lines. Larger nodes and redder colors indicate greater connectivity of genes in the network.</p>
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13 pages, 2645 KiB  
Article
Assessing the Effectiveness of Turf Transplantation and Artificial Replanting in Restoring Abandoned Mining Areas
by Amannisa Kuerban, Guankui Gao, Abdul Waheed, Hailiang Xu, Shuyu Wang and Zewen Tong
Sustainability 2024, 16(20), 8977; https://doi.org/10.3390/su16208977 - 17 Oct 2024
Viewed by 187
Abstract
Long-term and extensive mineral mining in the Kuermutu mine section of the Two Rivers Nature Reserve in the Altai region has disrupted the ecological balance between soil and vegetation. To assess the effectiveness of various restoration measures in this abandoned mine area, we [...] Read more.
Long-term and extensive mineral mining in the Kuermutu mine section of the Two Rivers Nature Reserve in the Altai region has disrupted the ecological balance between soil and vegetation. To assess the effectiveness of various restoration measures in this abandoned mine area, we compared two restoration approaches—natural turf transplantation (NTT) and replanted economic crop grassland (ARGC)—against an unaltered control (original grassland). We employed 11 evaluation indices to conduct soil and vegetation surveys. We developed a comprehensive evaluation model using the Analytic Hierarchy Process (AHP) to assess restoration outcomes for each grassland type. Our findings indicate that both NTT and ARGC significantly improved ecological conditions, such as reducing soil fine particulate matter loss and restoring vegetation cover. This brought these areas closer to their original grassland state. The species composition and community structure of the NTT and ARGC vegetation communities improved relative to the original grassland. This was due to a noticeable increase in dominant species’ importance value. Vegetation cover averaged higher scores in NTT, while the average height was greater in ARGC. The soil water content and soil organic carbon (SOC) varied significantly with depth (p < 0.05), following a general ‘V’ pattern. NTT positively impacted soil moisture content (SMC) at the surface, whereas ARGC influenced SMC in deeper layers, with the 40–50 cm soil layer achieving 48.13% of the original grassland’s SMC. SOC levels were highest in the control (original grassland), followed by ARGC and NTT, with ARGC showing the greatest organic carbon content at 20–30 cm depths. A comprehensive AHP ecological-economic evaluation revealed that restoration effectiveness scores were 0.594 for NTT and 0.669 for ARGC, translating to 59.4% and 66.9%, respectively. ARGC restoration was found to be more effective than NTT. These results provide valuable insights into ecological restoration practices for abandoned mines in Xinjiang and can guide future effectiveness evaluations. Full article
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<p>Study area.</p>
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<p>Vegetation coverage (<b>a</b>) and mean height (<b>b</b>) of different types of grasslands. Note: Different lowercase letters indicate significant differences between different types of grasslands at the 0.05 level. NG, natural grassland; NTT, natural turf transplantation; ARCG, artificial replanting of cash crop grassland; this is applicable for the following figures as well.</p>
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<p>Changes in diversity indices of vegetation communities in different grassland types (<b>a</b>–<b>d</b>). “NS” indicated that the grassland type diversity indices of the restored NTT and ARCG were not significantly different from those of the original grassland, illustrating that the restoration was effective.</p>
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<p>Effect of restoration of natural turf-transplanted grassland and replanted cash crop blackcurrant grassland.</p>
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24 pages, 14015 KiB  
Article
CDP-MVS: Forest Multi-View Reconstruction with Enhanced Confidence-Guided Dynamic Domain Propagation
by Zitian Liu, Zhao Chen, Xiaoli Zhang and Shihan Cheng
Remote Sens. 2024, 16(20), 3845; https://doi.org/10.3390/rs16203845 - 16 Oct 2024
Viewed by 274
Abstract
Using multi-view images of forest plots to reconstruct dense point clouds and extract individual tree parameters enables rapid, high-precision, and cost-effective forest plot surveys. However, images captured at close range face challenges in forest reconstruction, such as unclear canopy reconstruction, prolonged reconstruction times, [...] Read more.
Using multi-view images of forest plots to reconstruct dense point clouds and extract individual tree parameters enables rapid, high-precision, and cost-effective forest plot surveys. However, images captured at close range face challenges in forest reconstruction, such as unclear canopy reconstruction, prolonged reconstruction times, insufficient accuracy, and issues with tree duplication. To address these challenges, this paper introduces a new image dataset creation process that enhances both the efficiency and quality of image acquisition. Additionally, a block-matching-based multi-view reconstruction algorithm, Forest Multi-View Reconstruction with Enhanced Confidence-Guided Dynamic Domain Propagation (CDP-MVS), is proposed. The CDP-MVS algorithm addresses the issue of canopy and sky mixing in reconstructed point clouds by segmenting the sky in the depth maps and setting its depth value to zero. Furthermore, the algorithm introduces a confidence calculation method that comprehensively evaluates multiple aspects. Moreover, CDP-MVS employs a decentralized dynamic domain propagation sampling strategy, guiding the propagation of the dynamic domain through newly defined confidence measures. Finally, this paper compares the reconstruction results and individual tree parameters of the CDP-MVS, ACMMP, and PatchMatchNet algorithms using self-collected data. Visualization results show that, compared to the other two algorithms, CDP-MVS produces the least sky noise in tree reconstructions, with the clearest and most detailed canopy branches and trunk sections. In terms of parameter metrics, CDP-MVS achieved 100% accuracy in reconstructing tree quantities across the four plots, effectively avoiding tree duplication. The accuracy of breast diameter extraction values of point clouds reconstructed by CDPMVS reached 96.27%, 90%, 90.64%, and 93.62%, respectively, in the four sample plots. The positional deviation of reconstructed trees, compared to ACMMP, was reduced by 0.37 m, 0.07 m, 0.18 m and 0.33 m, with the average distance deviation across the four plots converging within 0.25 m. In terms of reconstruction efficiency, CDP-MVS completed the reconstruction of the four plots in 1.8 to 3.1 h, reducing the average reconstruction time per plot by six minutes compared to ACMMP and by two to three times compared to PatchMatchNet. Finally, the differences in tree height accuracy among the point clouds reconstructed by the different algorithms were minimal. The experimental results demonstrate that CDP-MVS, as a multi-view reconstruction algorithm tailored for forest reconstruction, shows promising application potential and can provide valuable support for forestry surveys. Full article
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<p>Overview of the study area. (<b>A</b>) Dongsheng Bajia Country Park—poplar; (<b>B</b>) Jiufeng—pine; (<b>C</b>) Olympic Forest Park—elm; (<b>D</b>) Olympic Forest Park—ginkgo.</p>
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<p>Comparison of camera position trajectories generated by Colmap. (<b>A</b>) Filming method with two circular paths. (<b>B</b>) Filming method with a single circular path around the forest plot.</p>
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<p>Technical framework.</p>
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<p>Comparison of sparse reconstruction point clouds under two filming methods. (<b>A</b>) Single circular path around the forest plot. (<b>B</b>) Two circular paths inside and outside the forest plot.</p>
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<p>Adaptive checkerboard propagation scheme of ACMMP. (Each V-shaped region contains 7 sampling pixels, and each strip region contains 11 sampling pixels. In the figure, Circles represent pixels. The black solid circle indicates the pixel to be estimated. The yellow circle represents the sampling point. During each propagation, the depth value of the red pixel is updated by the black pixel, and vice versa.).</p>
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<p>CDP-MVS dynamic domain propagation scheme (removing the central sample points and independently sampling in eight directions. Circles represent pixels. The black solid circle indicates the pixel to be estimated. During each propagation, the depth value of the red pixel is updated by the black pixel, and vice versa.).</p>
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<p>Reprojection flowchart. (The yellow line represents the process of projecting the pixel point p of the reference image to the point q in the adjacent image. The green line represents the process of re-projecting the point q back to the reference image.).</p>
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<p>Reference image (<b>A</b>) and its binarized grayscale image with sky segmentation (<b>B</b>).</p>
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<p>CDP-MVS algorithm flowchart.</p>
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<p>PatchMatchNet propagation sampling strategy. (Circles represent pixels. The black solid circle indicates the pixel to be estimated. During each propagation, the depth value of the red pixel is updated by the black pixel, and vice versa.).</p>
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<p>Dense point clouds reconstructed for three plots using different algorithms. (<b>a</b>) Poplar, (<b>b</b>) pine, (<b>c</b>) elm, (<b>d</b>) ginkgo. 1: CDP-MVS, 2: ACMMP, 3: PatchMatchNet.</p>
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<p>Dense point clouds reconstructed for three plots using different algorithms. (<b>a</b>) Poplar, (<b>b</b>) pine, (<b>c</b>) elm, (<b>d</b>) ginkgo. 1: CDP-MVS, 2: ACMMP, 3: PatchMatchNet.</p>
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<p>Comparison of canopy details reconstructed by different algorithms. (<b>a</b>) Poplar, (<b>b</b>) pine, (<b>c</b>) elm, (<b>d</b>) ginkgo. 1: CDP-MVS, 2: ACMMP, 3: PatchMatchNet.</p>
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<p>Comparison of canopy details reconstructed by different algorithms. (<b>a</b>) Poplar, (<b>b</b>) pine, (<b>c</b>) elm, (<b>d</b>) ginkgo. 1: CDP-MVS, 2: ACMMP, 3: PatchMatchNet.</p>
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<p>Comparison of trunk details reconstructed by different algorithms. (<b>a</b>) Poplar, (<b>b</b>) pine, (<b>c</b>) elm, (<b>d</b>) ginkgo. 1: CDP-MVS, 2: ACMMP, 3: PatchMatchNet.</p>
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<p>Comparison of trunk details reconstructed by different algorithms. (<b>a</b>) Poplar, (<b>b</b>) pine, (<b>c</b>) elm, (<b>d</b>) ginkgo. 1: CDP-MVS, 2: ACMMP, 3: PatchMatchNet.</p>
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<p>Scatter plot comparing reconstructed tree positions with actual positions (unit: meters). (<b>a</b>) Poplar, (<b>b</b>) pine, (<b>c</b>) elm, (<b>d</b>) ginkgo. 1: CDP-MVS, 2: ACMMP, 3: PatchMatchNet.</p>
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<p>Scatter plot comparing reconstructed tree positions with actual positions (unit: meters). (<b>a</b>) Poplar, (<b>b</b>) pine, (<b>c</b>) elm, (<b>d</b>) ginkgo. 1: CDP-MVS, 2: ACMMP, 3: PatchMatchNet.</p>
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21 pages, 3449 KiB  
Article
Effects of Different Additives on the Chemical Composition, Fermentation Quality, Bacterial Community and Gene Function Prediction of Caragana korshinskii Kom. Silage
by Yuxiang Wang, Manlin Wei, Fuyu Yang, Haiying Zheng, Junjie Gao, Wen Peng, Ming Xiao, Runze Zhang and Yongjie Zheng
Agronomy 2024, 14(10), 2386; https://doi.org/10.3390/agronomy14102386 - 15 Oct 2024
Viewed by 296
Abstract
The aim of this study was to investigate the effects of Lentilactobacillus plantarum (LP), cellulase (CE), and xylanase (XE) supplementation on the fermentation quality, chemical composition, and bacterial community of Caragana korshinskii Kom. silage. Four groups were designed for the study. No additives [...] Read more.
The aim of this study was to investigate the effects of Lentilactobacillus plantarum (LP), cellulase (CE), and xylanase (XE) supplementation on the fermentation quality, chemical composition, and bacterial community of Caragana korshinskii Kom. silage. Four groups were designed for the study. No additives were used in the control group (CK), and LP (1 × 106 cfu/g), CE (1 × 104 IU/g) and XE (2 × 105 IU/g) were added to the experimental groups on a fresh matter basis, with three replicates per group. To promote fermentation, 5% molasses was added to all of the groups. On days 15 and 60, fermentation quality, chemical composition and the bacterial community were analysed. The pH of groups CE and XE was lower than that of the CK group at 60 days. During ensiling, the lactic acid (LA) content in the experimental groups and the acetic acid (AA) content in the CK and LP groups increased. At 60 days, the dominant genera in the CK and LP groups was Weissella and the dominant genera in the CE and XE groups was Lentilactobacillus. At different times during silage, nucleotide metabolism was enhanced, whereas the metabolism of carbohydrate, amino acids, energy, cofactors and vitamins was inhibited in the LP group. However, the metabolism of amino acids, energy, cofactors and vitamins in the CE and XE groups was increased, whereas the metabolism of nucleotides was inhibited. In conclusion, LP, CE and XE could exert a positive effect on the fermentation quality of C. korshinskii Kom. silage by shifting the bacterial community composition. Full article
(This article belongs to the Section Agricultural Biosystem and Biological Engineering)
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<p>Venn diagram of the bacterial species. CK, control; LP, <span class="html-italic">Lentilactobacillus plantarum</span>; CE, cellulase; XE, xylanase. The numbers behind CK, LP, CE, and XE represent the days of ensiling.</p>
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<p>PCoA of the bacterial species diversity in <span class="html-italic">C. korshinskii</span> Kom. silage at 15 days (<b>A</b>) and 60 days (<b>B</b>). CK, control; LP, <span class="html-italic">Lentilactobacillus plantarum</span>; CE, cellulase; XE, xylanase. The numbers behind CK, LP, CE, and XE represent the days of ensiling.</p>
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<p>Distribution of bacterial communities at the phylum (<b>A</b>) and genus (<b>B</b>) levels at days 15 and 60 in <span class="html-italic">C. korshinskii</span> Kom. silage. Small populations with abundances less than 0.01 were combined as others. CK, control; LP, <span class="html-italic">Lentilactobacillus plantarum</span>; CE, cellulase; XE, xylanase. The numbers behind CK, LP, CE, and XE represent the days of ensiling.</p>
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<p>Species differences in bacterial genera (LDA = 3) between 15 days (<b>A</b>) and 60 days (<b>B</b>) of ensiling. CK, control; LP, <span class="html-italic">Lentilactobacillus plantarum</span>; CE, cellulase; XE, xylanase. The numbers behind CK, LP, CE, and XE represent the days of ensiling.</p>
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<p>Species differences in bacterial genera (LDA = 3) between 15 days (<b>A</b>) and 60 days (<b>B</b>) of ensiling. CK, control; LP, <span class="html-italic">Lentilactobacillus plantarum</span>; CE, cellulase; XE, xylanase. The numbers behind CK, LP, CE, and XE represent the days of ensiling.</p>
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<p>Heatmap of the Spearman correlation coefficients of chemical composition, fermentation quality and bacterial genera of <span class="html-italic">C. korshinskii</span> Kom. silage at 15 (<b>A</b>) and 60 (<b>B</b>) days. The colour of the heatmap indicates the Spearman correlation coefficient “R” (−1 to 1). R &gt; 0 indicates a positive correlation, and R &lt; 0 indicates a negative correlation. *, 0.01 &lt; <span class="html-italic">p</span> &lt; 0.05; **, 0.001 &lt; <span class="html-italic">p</span> &lt; 0.01; ***, <span class="html-italic">p</span> &lt; 0.001. CK, control; LP, <span class="html-italic">Lentilactobacillus plantarum</span>; CE, cellulase; XE, xylanase. The numbers behind CK, LP, CE, and XE represent the days of ensiling.</p>
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<p>Predicted pathways of the bacterial community in <span class="html-italic">C. korshinskii</span> Kom. at 15 days and 60 days of ensiling. (<b>A</b>) the first metabolic pathway at 15 days of <span class="html-italic">C. korshinskii</span> Kom. Silage. (<b>B</b>) the first metabolic pathway at 60 days of <span class="html-italic">C. korshinskii</span> Kom. Silage. (<b>C</b>) the second metabolic pathway at 15 days of <span class="html-italic">C. korshinskii</span> Kom. Silage. (<b>D</b>) the second metabolic pathway at 60 days of <span class="html-italic">C. korshinskii</span> Kom. Silage. (<b>E</b>) carbohydrate metabolism of the third pathway level at 15 days of <span class="html-italic">C. korshinskii</span> Kom. Silage. (<b>F</b>) carbohydrate metabolism of the third pathway level at 60 days of <span class="html-italic">C. korshinskii</span> Kom. Silage. CK, control; LP, <span class="html-italic">Lentilactobacillus plantarum</span>; CE, cellulase; XE, xylanase. The numbers behind CK, LP, CE, and XE represent the days of ensiling.</p>
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15 pages, 2574 KiB  
Article
The Distribution, Population Size, and Habitat Preferences of a Newly Established Population of the Oriental Magpie Pica serica in Tomakomai City, Hokkaido, Northern Japan
by Masahiro Fujioka and Hisaya Murayama
Birds 2024, 5(4), 656-670; https://doi.org/10.3390/birds5040045 - 15 Oct 2024
Viewed by 273
Abstract
Non-native species have caused various problems for both animal and human communities globally, but their monitoring during the early stages of establishment is often difficult. A population of the Oriental Magpie (Pica serica) has established on Hokkaido Island, northern Japan, since [...] Read more.
Non-native species have caused various problems for both animal and human communities globally, but their monitoring during the early stages of establishment is often difficult. A population of the Oriental Magpie (Pica serica) has established on Hokkaido Island, northern Japan, since the 1990s, offering a rare opportunity for field biologists to monitor the entire history of a colonizing avian population. To clarify the current number and distribution of the population and their major determinants, we conducted bimonthly surveys from May 2012 to March 2013, over a total of 417 h, in Tomakomai City, the central area of the current distribution. We found 181 to 248 magpies in every survey, and 46 active nests in May. Most of the magpies appeared in residential areas, avoiding commercial and industrial areas, and did not show seasonal changes in their distribution pattern. The magpies mainly foraged in short grasslands in public spaces, such as parks, in May and July, but most of the birds preferred house gardens for foraging from November to March. Dogs or cats were often kept outside in the gardens where the magpies foraged, and observations of magpies stealing and hoarding pet food were common. It is likely that the magpies rely on anthropogenic food resources such as pet food, especially in winter. Continuous monitoring of this population will enable further knowledge of the factors that limit the number and range of not only non-native species but also avian populations in general to be obtained. Full article
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<p>The study area, with the locations of active nests of the Oriental Magpie in May 2012 indicated by plus signs and those of roosts by blue circles (found in September 2012) or red squares (found in January 2013). The study area was divided into 11 blocks based on the combination of four sub-areas, of which names are shown in text boxes (West, Central, Utonai and Yufutsu), and four categories of zones in the Urban Planning of Tomakomai City (see <a href="#birds-05-00045-t001" class="html-table">Table 1</a>). The background map is a grayscale-converted ©OpenStreetMap, wherein the dark gray represents forested areas.</p>
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<p>The locations where Oriental Magpies were found in May (red triangles), September (orange circles), and January (blue inverted triangles). The symbol size is roughly proportional to the flock size.</p>
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<p>Seasonal change in the foraging microhabitat of Oriental Magpies in Tomakomai City. ”Others” were mostly on snow in January and March. Sample sizes are given above the bars. “Rndm” means random points.</p>
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15 pages, 1715 KiB  
Article
Effects of Different Additives and Ratios on Broom Sorghum Straw Silage Characteristics and Bacterial Communities
by Panjie Sheng, Baochao Bai, Mingjian Liu, Weiqin Ma, Jianliang Liu, Chaoran Song, Shuai Du, Gentu Ge, Yushan Jia and Zhijun Wang
Microorganisms 2024, 12(10), 2062; https://doi.org/10.3390/microorganisms12102062 (registering DOI) - 15 Oct 2024
Viewed by 316
Abstract
As a large agricultural country, China produces a large number of agricultural and sideline products while harvesting agricultural products every year. Crop straw is one of them. Broom sorghum is a traditional crop in China, which produces a large amount of straw resources [...] Read more.
As a large agricultural country, China produces a large number of agricultural and sideline products while harvesting agricultural products every year. Crop straw is one of them. Broom sorghum is a traditional crop in China, which produces a large amount of straw resources every year. These straw resources are placed in the field and cannot be used efficiently. The purpose of this study was to solve the problem of straw utilization of Broom sorghum, one of the main food crops in arid and semi-arid areas of northern China. Broom sorghum is not only a nutritious food crop, its straw is also rich in crude fiber and mineral elements, which has high utilization value. However, due to the high content of lignocellulose in straw, the texture is hard, which limits its digestion and utilization efficiency as feed. In this study, the broom sorghum straw was used as the research object, and the straw raw materials were treated with Lactobacillus plantarum, cellulase and xylanase, respectively. After silage fermentation for 30 d and 60 d, the bags were opened to determine the nutritional quality, fermentation quality, microbial community structure and other indicators. The best fermentation time and additives for broom sorghum straw silage were comprehensively screened to improve the nutritional value of straw and animal production performance. The results showed that the nutritional quality of silage straw increased with the extension of fermentation time. Compared with silage straw after 30 days of fermentation, the nutritional quality and fermentation quality of straw were significantly improved after 60 days of fermentation. Lactobacillus plantarum, cellulase and xylanase could improve the silage performance of broom sorghum straw by improving the microbial community structure in straw, and the effect of cellulase was the best. When cellulase was used in straw at the standard of 20 U/g FM, the content of water-soluble carbohydrates could be significantly increased to 31.35 g/kg FM, and the concentration of lactic acid was also significantly increased to 23.79 g/kg FM. Therefore, in actual production, it is recommended to use cellulase at a dose of 20 U/g FM in broom sorghum silage and open the bag after 60 days of silage fermentation. The results of this study provided a scientific basis for the efficient utilization of broom sorghum straw as feed. Full article
(This article belongs to the Section Veterinary Microbiology)
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<p>Effects of different additives and ensiling days on α diversity of broom sorghum straw silage. This figure shows the significant differences between the selected two groups of samples and marks the two groups with significant differences (0.01 &lt; <span class="html-italic">p</span> ≤ 0.05 marked as *, 0.001 &lt; <span class="html-italic">p</span> ≤ 0.01 marked as **, <span class="html-italic">p</span> ≤ 0.001 marked as ***). The abscissa is the grouping name, and the ordinate is the index size of each group. FM: fresh matter; CK1: CK fermentation for 30 days; CK2: CK fermentation 60 days; LP1: LP fermentation for 30 days; LP2: LP fermentation for 60 days; CE1: CE20 fermentation for 30 days; CE2: CE20 fermentation for 60 days; XE1: XE20 fermentation for 30 days; XE2: XE20 fermentation for 60 days. The same for both figures.</p>
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<p>PCoA analysis of different additives and ensiling days broom sorghum straw silage.</p>
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<p>Effects of different treatments on microbial community structure of broom sorghum straw silage at the phylum level. Note: (<b>A</b>): microbial species composition at phylum level; (<b>B</b>): Differences in microbial species composition between different treatments at the phylum level; (<b>C</b>): microbial species composition at genus level; (<b>D</b>): Differences in microbial species composition between different treatments at the genus level. 0.01 &lt; <span class="html-italic">p</span> ≤ 0.05 marked as *, 0.001 &lt; <span class="html-italic">p</span> ≤ 0.01 marked as **.</p>
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<p>Correlation analysis between microorganisms and fermentation indexes of broom sorghum straw silage.</p>
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<p>Prediction of 16S rRNA gene function of broom sorghum straw raw materials and silage samples after 60 days of fermentation. Note: (<b>A</b>): primary pathway level, (<b>B</b>): secondary pathway level, (<b>C</b>): tertiary pathway level; FM: straw raw materials; CK: control group; LP: <span class="html-italic">Lactobacillus plantarum</span> treatment; CE: cellulase treatment; XE: xylanase treatment.</p>
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18 pages, 5341 KiB  
Article
Prevalence and Diversity of Plant Parasitic Nematodes in Irish Peatlands
by Anusha Pulavarty, Tilman Klappauf, Ankit Singh, Patricia Molero Molina, Anique Godjo, Bastiaan Molleman, Douglas McMillan and Thomais Kakouli-Duarte
Diversity 2024, 16(10), 639; https://doi.org/10.3390/d16100639 (registering DOI) - 15 Oct 2024
Viewed by 301
Abstract
The prevalence of plant parasitic nematodes (PPN) in the Irish peatlands was investigated in five different peatland habitats—raised bog, cutover scrub/woodlands, fens and peat grasslands, which were further sub-categorised into fourteen different sub-habitats. Within the raised bog habitat were healthy bog hummock (HBH), [...] Read more.
The prevalence of plant parasitic nematodes (PPN) in the Irish peatlands was investigated in five different peatland habitats—raised bog, cutover scrub/woodlands, fens and peat grasslands, which were further sub-categorised into fourteen different sub-habitats. Within the raised bog habitat were healthy bog hummock (HBH), healthy bog lawn (HBL), degraded bog hummock (DBH) and degraded bog lawn (DBL) and the fen habitats were fen peat (FP) and rich fen peat (R-FP). Cutover scrub or woodland habitat included cutover scrub rewetted (C-RW), cutover scrub non-rewetted (C-NRW), woodlands rewetted (W-RW) and woodlands non-rewetted (W-NRW). Grassland included wasted peat (WP), rough grazing (RG-I) and improved fen peat grassland (IFPG-RW and IFPG-NRW). Soil samples from peatlands were all collected between July and December 2023 when the temperature ranged from 12 to 20 °C. One half of each sample was used for molecular nematode analysis and the other half for morphological identification of nematodes. For the morphological identification, a specific nematode extraction protocol was optimised for peatland soils, and the extracted nematodes were fixed onto slides to be studied under a high-power light microscope. Subsequently, the other part of the soil was processed to isolate total DNA, from which the 18S rRNA gene was sequenced for the identification of nematode taxa. The extracted DNA was also used for randomly amplified polymorphic DNA (RAPD) fingerprinting analysis to determine banding patterns that could classify different bog habitats based on PPN random primers. Compared to that in the climax habitats (HBH, HBL, DBH, DBL, FP, R-FP), PPN prevalence was recorded as being higher in grasslands (WP, RG-I, IFPG-RW and IFPG-NRW) and scrub/woodland ecosystems (C-RW, C-NRW, W-RW, W-NRW). The results indicate that nematode populations are different across the various bog habitats. Emerging and current quarantine PPN belonging to the families Pratylenchidae, Meloidogynidae, Anguinidae and Heteroderidae were noted to be above the threshold limits mentioned under EPPO guidelines, in grassland and wooded peatland habitats. Future actions for PPN management may need to be considered, along with the likelihood that these PPN might impact future paludiculture and other crops and trees growing in nearby agricultural lands. Full article
(This article belongs to the Section Biodiversity Conservation)
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<p>(<b>a</b>) Approximate site location in the Republic of Ireland; (<b>b</b>) Bog sampling location and bog habitats in each location, (i) 53°01′14.2″ N and 7°57′15.5″ W, (ii) 53°05′14.01″ N and 7°87′69.96″ W, (iii) 53°06′08.4″ N and 7°80′08.4″ W; source Google Maps.</p>
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<p>RAPD profile of peat habitats: (<b>a</b>) Healthy bog lawn (HBH), (<b>b</b>) Rich Fen peat (R-FP) obtained with primers A5, A6, A7, A9, A10, A12, A13, A15, A16, A18, A19, A20, A22, A24. M = Molecular weight marker (Promega 1 Kb Ladder (G571A)).</p>
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<p>Dendrogram showing the proximity distance between various peatland habitats based on RAPD index data (constructed using IBM SPSS (version 29.0.1.0 (171)).</p>
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<p>Heat map showing the abundance of different nematode families detected in various peat habitats. The PPN families are highlighted using red ovals.</p>
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<p>Relative abundance of PPN (%) in different peatland habitats (molecular data). Values represented by similar letters are not significantly different from each other in terms of PPN % (<span class="html-italic">p</span> ≤ 0.05).</p>
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19 pages, 16931 KiB  
Article
Effects of Differentially Methylated CpG Sites in Enhancer and Promoter Regions on the Chromatin Structures of Target LncRNAs in Breast Cancer
by Zhiyu Fan, Yingli Chen, Dongsheng Yan and Qianzhong Li
Int. J. Mol. Sci. 2024, 25(20), 11048; https://doi.org/10.3390/ijms252011048 (registering DOI) - 15 Oct 2024
Viewed by 472
Abstract
Aberrant DNA methylation plays a crucial role in breast cancer progression by regulating gene expression. However, the regulatory pattern of DNA methylation in long noncoding RNAs (lncRNAs) for breast cancer remains unclear. In this study, we integrated gene expression, DNA methylation, and clinical [...] Read more.
Aberrant DNA methylation plays a crucial role in breast cancer progression by regulating gene expression. However, the regulatory pattern of DNA methylation in long noncoding RNAs (lncRNAs) for breast cancer remains unclear. In this study, we integrated gene expression, DNA methylation, and clinical data from breast cancer patients included in The Cancer Genome Atlas (TCGA) database. We examined DNA methylation distribution across various lncRNA categories, revealing distinct methylation characteristics. Through genome-wide correlation analysis, we identified the CpG sites located in lncRNAs and the distally associated CpG sites of lncRNAs. Functional genome enrichment analysis, conducted through the integration of ENCODE ChIP-seq data, revealed that differentially methylated CpG sites (DMCs) in lncRNAs were mostly located in promoter regions, while distally associated DMCs primarily acted on enhancer regions. By integrating Hi-C data, we found that DMCs in enhancer and promoter regions were closely associated with the changes in three-dimensional chromatin structures by affecting the formation of enhancer–promoter loops. Furthermore, through Cox regression analysis and three machine learning models, we identified 11 key methylation-driven lncRNAs (DIO3OS, ELOVL2-AS1, MIAT, LINC00536, C9orf163, AC105398.1, LINC02178, MILIP, HID1-AS1, KCNH1-IT1, and TMEM220-AS1) that were associated with the survival of breast cancer patients and constructed a prognostic risk scoring model, which demonstrated strong prognostic performance. These findings enhance our understanding of DNA methylation’s role in lncRNA regulation in breast cancer and provide potential biomarkers for diagnosis. Full article
(This article belongs to the Section Molecular Oncology)
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<p>Probe annotation and methylation features of lncRNAs. (<b>A</b>) Number of DNA methylation probes and lncRNAs for five lncRNA categories. (<b>B</b>) Expression levels of five lncRNA categories across tumor and normal samples. (<b>C</b>) Global methylation value distribution of five lncRNA categories across tumor and normal samples. (<b>D</b>) DNA methylation patterns of protein-coding genes, lncRNAs, and miRNAs across the gene body and ±5 kb flanking regions of the gene body. (<b>E</b>) DNA methylation patterns of five different categories of lncRNAs across the gene body and ±5 kb flanking the gene body. Analyses utilized TCGA-BRCA DNA methylation and gene expression data. Statistical significance was assessed using the <span class="html-italic">t</span>-test (* <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001).</p>
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<p>Genomic location of proximal and distally associated CpGs of lncRNAs according to ChromHMM and TF binding regions (<b>A</b>) Bar plot showing the enrichment of distally associated CpGs of lncRNAs across functional regulatory regions based on MCF-7 ChromHMM annotation. The bars represent the ratio of observed to expected frequencies for distal CpGs. (<b>B</b>) Enrichment of the proximal CpGs of lncRNAs in functional regulatory regions. (<b>C</b>) Functional annotation of the lncRNAs with DMCs in the relevant enhancer regions. Top 20 clusters with their representative enriched terms (colored by cluster ID), where nodes that share the same cluster ID are typically close to each other. (<b>D</b>) Network plot of the lncRNAs with DMCs in promoter regions. Data obtained from MCF-7 ChromHMM annotation and Metascape analysis.</p>
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<p>Assessment of prognostic values in the TCGA-BRCA, GSE20711, and GSE20685 datasets. Comparison of the OS status of breast cancer patients with varying risk scores, and K–M curves in (<b>A</b>) TCGA-BRCA, (<b>B</b>) GSE20711, and (<b>C</b>) GSE20685 datasets. The AUC values for the time-dependent ROC curves depict the OS prediction values for the (<b>D</b>) TCGA-BRCA, (<b>E</b>) GSE20711, and (<b>F</b>) GSE20685 datasets. Statistical significance was determined using the log-rank test for K–M curves and the concordance index (C-index) for AUC calculations.</p>
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<p>Determination of the independent prognostic value of risk model (<b>A</b>) A signature-based nomogram was applied to estimate 1-, 3-, and 5-year overall survival probabilities.(* <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01, *** <span class="html-italic">p</span> &lt; 0.001). (<b>B</b>) Calibration plots of the nomogram for predicting the 1-, 3-, and 5-year OS. (<b>C</b>) The C-index was utilized to assess and compare the prognostic accuracy between clinical factors and the risk score. (<b>D</b>) Subgroup analysis of the Kaplan–Meier (K–M) survival curves was conducted using the log-rank test based on factors such as age, histopathological grade, and clinical stage. All results were based on the TCGA-BRCA dataset.</p>
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<p>Effect of DMCs on enhancer–promoter looping and DP-lncRNA TMEM220-AS1 expression. Hi-C contact maps for the regions of chromosome 17 (10.224 Mb–11.224 Mb) at 10 kb resolution in the (<b>A</b>) MCF-7 cell lines and (<b>B</b>) HMEC cell lines; purple points indicate chromatin loops in the HMEC and MCF-7 cell lines, respectively; red rectangles represent TMTM22–AS1; green rectangles indicate significant CpG sites. (<b>C</b>) Genome browser snapshots of TMEM220-AS1 in the MCF-7 cell lines, the purple vertical bars highlight the important loop anchor regions which are associated with DP-lncRNAs. The promoter of TMEM220-AS1 co-localize with the anchor of important chromatin loop, DNase-seq peaks, and histone (H3K27ac, H3K4me1) ChIP-seq peaks, and (<b>D</b>) genome browser snapshots of TMEM220-AS1 in the HMEC cell lines. Hi-C data were obtained from the ENCODE database, and snapshots were generated using the Washu Epigenome Browser.</p>
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<p>DNA methylation affects 3D genome architecture through distal enhancers. (<b>A</b>) Hi-C contact maps of C9orf163 in the MCF-7 cell lines and (<b>B</b>) HMEC cell lines. (<b>C</b>) Hi-C contact maps of HID1-AS1 in the MCF-7 cell lines and (<b>D</b>) HMEC cell lines. Hi-C data were obtained from the ENCODE database. (Purple point: chromatin loops; Red: lncRNAs; Green: significantly different CpG sites, Blue: enhancer regions.).</p>
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<p>Relationships between immune cell infiltration, the TME, and the key methylation-driven lncRNA signature. (<b>A</b>) Heat map of immune responses among the high- and low-risk groups based on the CIBERSORT, ESTIMATE, and ssGSEA algorithms. (<b>B</b>) Comparison of TME scores in both risk groups via the ESTIMATE algorithm. (<b>C</b>) Box plot comparing 13 immune-linked functions in both risk groups. (<b>D</b>) The CIBERSORT algorithm was used to quantify the distribution of 22 tumor-infiltrating immune cells in all HNSCC patients. (<b>E</b>) Violin plot showing the fraction of 22 immune cells in both risk groups. Statistical significance was assessed using the <span class="html-italic">t</span>-test (* <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01, and *** <span class="html-italic">p</span> &lt; 0.001).</p>
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<p>Classification of lncRNAs based on their genomic proximity to neighboring transcripts [<a href="#B50-ijms-25-11048" class="html-bibr">50</a>].</p>
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