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

Years

Between: -

Subjects

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Journals

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Article Types

Countries / Regions

remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline
remove_circle_outline

Search Results (2,089)

Search Parameters:
Keywords = tropical forest

Order results
Result details
Results per page
Select all
Export citation of selected articles as:
27 pages, 23239 KiB  
Article
Integration of Structural Characteristics from GEDI Waveforms for Improved Forest Type Classification
by Mary M. McClure, Satoshi Tsuyuki and Takuya Hiroshima
Remote Sens. 2024, 16(24), 4776; https://doi.org/10.3390/rs16244776 (registering DOI) - 21 Dec 2024
Abstract
Abstract: Forest types correspond to differences in structural characteristics and species composition that influence biomass and biodiversity values, which are essential measurements for ecological monitoring and management. However, differentiating forest types in tropical regions remains a challenge. This study aimed to improve forest [...] Read more.
Abstract: Forest types correspond to differences in structural characteristics and species composition that influence biomass and biodiversity values, which are essential measurements for ecological monitoring and management. However, differentiating forest types in tropical regions remains a challenge. This study aimed to improve forest type extent mapping by combining structural information from discrete full-waveform LiDAR returns with multitemporal images. This study was conducted in a tropical forest region over complex terrain in north-eastern Tanzania. First, structural classes were generated by applying time-series clustering algorithms. The results showed four different structural clusters corresponding to forest types, montane–humid forest, montane–dry forest, submontane forest, and non-forest, when using the Kshape algorithm. Kshape considers the shape of the full-sequence LiDAR waveform, requiring little preprocessing. Despite the overlap amongst the original clusters, the averages of structural characteristics were significantly different across all but five metrics. The labeled clusters were then further refined and used as training data to generate a wall-to-wall forest cover type map by classifying biannual images. The highest-performing model was a KNN model with 13 spectral and 3 terrain features achieving 81.7% accuracy. The patterns in the distributions of forest types provide better information from which to adapt forest management, particularly in forest–non-forest transitional zones. Full article
(This article belongs to the Section Environmental Remote Sensing)
17 pages, 2832 KiB  
Article
Effects of Close-to-Nature Transformation of Plantations on Eco-Hydrological Function in Hainan Tropical Rainforest National Park
by Aohua Yang, Guijing Li, Wencheng Peng, Long Wan, Xiqiang Song, Yuguo Liu and Shouqian Nong
Water 2024, 16(24), 3692; https://doi.org/10.3390/w16243692 (registering DOI) - 21 Dec 2024
Abstract
Girdling is a crucial technique for promoting the close-to-nature transformation of plantation forests in Hainan Tropical Rainforest National Park (HNNP). It has shown effectiveness in aspects such as community structure and biodiversity restoration. However, its impacts on ecological functions like eco-hydrology still require [...] Read more.
Girdling is a crucial technique for promoting the close-to-nature transformation of plantation forests in Hainan Tropical Rainforest National Park (HNNP). It has shown effectiveness in aspects such as community structure and biodiversity restoration. However, its impacts on ecological functions like eco-hydrology still require further in-depth investigation. This study analyzes the impact of girdling on the eco-hydrological indices of three plantations—Acacia mangium, Pinus caribaea, and Cunninghamia lanceolata—through field investigations and laboratory tests. The data was evaluated using a game theory combination weighting-cloud model. The results show that the eco-hydrological indicators of leaf litter in A. mangium increased by 5.77% while those of P. caribaea and C. lanceolata decreased by 11.86% and 5.29%, respectively. Soil bulk density decreased slightly across all plantations while total porosity increased, with A. mangium showing the highest increase of 20.31%. Organic carbon content increased by 76.81% in A. mangium and 7.24% in C. lanceolata, whereas it decreased in P. caribaea. Saturated hydraulic conductivity increased by 33.32% in P. caribaea and 20.91% in A. mangium but decreased in C. lanceolata. Based on the cloud model, the eco-hydrological function of A. mangium improved from ‘medium’ to ‘good’, while that of P. caribaea and C. lanceolata declined towards the ‘poor’ level. In summary, during the process of close-to-nature transformation of tropical rainforests, girdling is an effective method to enhance the ecohydrological functions of broadleaf planted forests. However, for coniferous species, the ecohydrological functions of the planted forests weaken in the short term following the transformation. Full article
(This article belongs to the Section Ecohydrology)
Show Figures

Figure 1

Figure 1
<p>Study area map.</p>
Full article ">Figure 2
<p>Pictures of different plantations before and after the close-to-nature transformation through girdling. (<b>a</b>) Before girdling of <span class="html-italic">Acacia mangium</span> plantations; (<b>b</b>) After girdling of <span class="html-italic">Acacia mangium</span> plantations; (<b>c</b>) Before girdling of <span class="html-italic">Cunninghamia lanceolata</span> plantations; (<b>d</b>) After girdling of <span class="html-italic">Cunninghamia lanceolata</span> plantations; (<b>e</b>) After girdling of <span class="html-italic">Pinus caribaea</span> plantations; (<b>f</b>) Before girdling of <span class="html-italic">Pinus caribaea</span> plantations.</p>
Full article ">Figure 3
<p>Litter water holding capacity, litter water absorption rate and soaking time process curve: (<b>a</b>) Litter water holding capacity and soaking time process curve; (<b>b</b>) Litter water absorption rate and soaking time process curve.</p>
Full article ">Figure 4
<p>Comprehensive evaluation cloud model map of eco-hydrological function; (<b>a</b>): Standard cloud model of eco-hydrological function of different plantations in Hainan Tropical Rainforest National Park; (<b>b</b>): <span class="html-italic">A. mangium</span> plantation eco-hydrological function cloud model diagram; (<b>c</b>): Cloud model diagram of eco-hydrological function of <span class="html-italic">C. lanceolata</span> plantation; (<b>d</b>): Cloud model diagram of eco-hydrological function of <span class="html-italic">P. caribaea</span> plantation.</p>
Full article ">
18 pages, 11826 KiB  
Article
Assessment of Native Wild Macromycete Strains for Mycoremediation of Copper-Contaminated Soils in Coffee Plantations
by Areli Castellanos De La Cruz, Clara Ivette Rincón-Molina, Luis Alberto Manzano-Gómez, Víctor Manuel Ruiz-Valdiviezo, Adriana Gen-Jiménez, Juan José Villalobos-Maldonado, Francisco Alexander Rincón-Molina, Eduardo Garrido-Ramírez and Reiner Rincón-Rosales
Horticulturae 2024, 10(12), 1376; https://doi.org/10.3390/horticulturae10121376 (registering DOI) - 21 Dec 2024
Abstract
This study evaluates the mycoremediation potential of wild mushroom species from Chiapas, Mexico, specifically for high copper concentrations. Nine fungal carpophores were collected from tropical forests near coffee plantations. The morphological characteristics of the fungal strains and fruiting bodies were analyzed. Each specimen [...] Read more.
This study evaluates the mycoremediation potential of wild mushroom species from Chiapas, Mexico, specifically for high copper concentrations. Nine fungal carpophores were collected from tropical forests near coffee plantations. The morphological characteristics of the fungal strains and fruiting bodies were analyzed. Each specimen was identified through sequencing using the ITS1 and ITS4 primers. The ability to tolerate different concentrations of copper was evaluated by determining the fungal mycelial growth inhibition potential. Copper bioaccumulation by the fungi was quantified using biosorption assays with atomic absorption spectrophotometry. The enzymatic activity of laccase, lignin peroxidase, and manganese peroxidase from the fungal species was also determined in the presence of copper. Phylogenetic analysis identified the fungal species as Agaricus bisporus, A. subrufescens, Calvatia fragilis, Ganoderma coffeatum, G. lucidum, Pleurotus djmor, P. floridanus, Trametes elegans, and T. versicolor, all classified within the Agaromycetes class. The nine fungal species exhibited varying abilities to tolerate Cu2+ concentrations from 30 to 100 mg L−1. At 30 and 60 mg L−1 Cu2+, the G. lucidum H14-35 strain demonstrated the highest biosorption capacity, reaching 76.97%. Overall, the mushrooms in this study showed strong Cu2⁺ tolerance and biosorption, making them promising biomaterials for remediating copper-contaminated soils. Full article
Show Figures

Figure 1

Figure 1
<p>Location of the study site and macromycete fungi collection.</p>
Full article ">Figure 2
<p>The percentage of fungal mycelial growth inhibition by different copper concentrations. Mean values of three replicates. Means followed by the same letter are non-significantly different (Tukey test, <span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">
25 pages, 1798 KiB  
Article
Fossil Hyaenanche Pollen from the Eocene of Kenya: The Paleophytogeograpy and Paleoclimate of a Relict Plant Genus Endemic to the Cape Province, South Africa
by Friðgeir Grímsson, Christian Geier, Johannes M. Bouchal, Silvia Ulrich, Reinhard Zetter and Manuel Vieira
Biology 2024, 13(12), 1079; https://doi.org/10.3390/biology13121079 (registering DOI) - 20 Dec 2024
Abstract
On the African continent, Picrodendraceae are represented by four genera. Their intracontinental paleophytogeographic histories and paleoecological aspects are obscured by the lack of pre-Miocene fossils. For this study, late Eocene sediments from Kenya were investigated. The sample was prepared in the laboratory, and [...] Read more.
On the African continent, Picrodendraceae are represented by four genera. Their intracontinental paleophytogeographic histories and paleoecological aspects are obscured by the lack of pre-Miocene fossils. For this study, late Eocene sediments from Kenya were investigated. The sample was prepared in the laboratory, and its organic residue was screened for pollen. We extracted fossil Picrodendraceae pollen and investigated the grains using light and scanning electron microscopy. Based on the pollen morphology, the grains were assigned to Hyaenanche. This genus is currently confined to a small area within the Cape Province, South Africa. There, the plants grow as shrubs and small trees at an elevation between 60 and 800 m, on rocky substrate, as part of open fynbos vegetation, and under a dry climate with hot summers and limited precipitation. The sedimentary context and the associated palynoflora suggest that during the Eocene of Kenya, Hyaenanche was part of lowland coastal vegetation in Eastern Africa. There, the plants grew under fully humid to winter-dry tropical climates as part of landwards margins of mangroves, seasonally inundated floodplain forests, or coastal forests. Our study shows that when evaluating paleoecological aspects of relict monotypic plants, their extant closely related genera and their fossil records need to be considered. Full article
(This article belongs to the Section Plant Science)
22 pages, 2753 KiB  
Article
Ant-Plant Mutualism in Mauritia flexuosa Palm Peat Swamp Forests: A Study of Host and Epiphyte Diversity in Ant Gardens
by Yakov Quinteros-Gómez, Jehoshua Macedo-Bedoya, Abel Salinas-Inga, Flavia Anlas-Rosado, Victor Santos-Linares, Geancarlo Alarcon-Iman, Doris Gómez-Ticerán, Franco Angeles-Alvarez, Sergio Olórtegui-Chamolí, Julio Solis-Sarmiento, Enoc Jara-Peña and Octavio Monroy-Vilchis
Insects 2024, 15(12), 1011; https://doi.org/10.3390/insects15121011 - 20 Dec 2024
Abstract
Mutualisms characterized by reciprocal benefits between species are a fundamental relationship of tropical ecosystems. Ant Gardens (AGs) represent an interesting ant-plant mutualism, involving specialized interactions between vascular epiphytes and ants. While this relationship has been extensively studied in various tropical regions, the available [...] Read more.
Mutualisms characterized by reciprocal benefits between species are a fundamental relationship of tropical ecosystems. Ant Gardens (AGs) represent an interesting ant-plant mutualism, involving specialized interactions between vascular epiphytes and ants. While this relationship has been extensively studied in various tropical regions, the available information on Peruvian ecosystems is limited. The objective of this study was to identify the ant and epiphyte species that constitute AGs. From February 2023 to January 2024, a study was conducted on two 50 × 10 m transects within the Mauritia flexuosa peat swamp forest, located within the Water Association Aguajal Renacal del Alto Mayo (ADECARAM) Tingana in San Martín, Peru. A total of 69 ant gardens were documented, comprising 18 phorophyte species, 19 epiphyte species, and three ant species. The results demonstrated that neither the height nor the diameter at breast height (DBH) of phorophytes exhibited a statistically significant correlation with the number of AGs per host. However, a positive correlation was observed between the length and width of the AGs and the number of ants per AG. The findings of this study contribute to the understanding of AG mutualism in Peruvian ecosystems. Full article
(This article belongs to the Special Issue Ecologically Important Symbioses in Insects)
15 pages, 2567 KiB  
Article
Wild Bee Diversity and Bee–Plant Interactions in Tropical and Temperate Forest Clearings in a Natural Protected Area in Central West Mexico
by Alvaro Edwin Razo-León, Alejandro Muñoz-Urias, Claudia Aurora Uribe-Mú, Francisco Martín Huerta-Martínez, Hugo Eduardo Fierros-López, Miguel Vásquez-Bolaños, Gustavo Moya-Raygoza and Pablo Carrillo-Reyes
Insects 2024, 15(12), 1009; https://doi.org/10.3390/insects15121009 - 20 Dec 2024
Abstract
Background: Bees rely on plants for nutrition and reproduction, making the preservation of natural areas crucial as pollinator reservoirs. Seasonal tropical dry forests are among the richest habitats for bees, but only 27% of their original extent remains in Mexico. In contrast, temperate [...] Read more.
Background: Bees rely on plants for nutrition and reproduction, making the preservation of natural areas crucial as pollinator reservoirs. Seasonal tropical dry forests are among the richest habitats for bees, but only 27% of their original extent remains in Mexico. In contrast, temperate forests harbor fewer bee species and face high deforestation rates, with 40% of their area converted to other land uses. This study aimed to estimate the α and β diversities of wild bees and compare bee–plant interaction networks between these two vegetation types. Methods: Wild bees and their interactions with plants were monitored for one year in four sites within the Área de Protección de Flora y Fauna Sierra de Quila. Two sites corresponded to seasonal tropical dry forest and two to temperate forest. α and β diversity, connectance, nestedness, web asymmetry, and niche overlap were analyzed. Results: Sierra de Quila harbors high bee diversity, with 155 species in tropical dry forest and 103 in temperate forest. Species turnover between vegetation types was high, although nine species used floral resources in both forests, connecting the interaction networks. Conclusions: Sierra de Quila diverse habitats promote high bee diversity, with niche partitioning and low connectance facilitating coexistence across different vegetation types. Full article
(This article belongs to the Section Social Insects)
Show Figures

Graphical abstract

Graphical abstract
Full article ">Figure 1
<p>Location of the APFFSQ (Sierra de Quila Flora and Fauna Protection Area) and sampling sites (SDTF—seasonally dry tropical forest, TF—temperate forest).</p>
Full article ">Figure 2
<p>Coverage—based rarefaction (solid line) and extrapolation (dashed line) plots with 95% confidence intervals (shaded areas) comparing (richness, q<sub>0</sub>), common species (q<sub>1</sub>), and dominant species (q<sub>2</sub>) on community bees between vegetation types (SDTF—seasonally dry tropical forest, TF—temperate forest).</p>
Full article ">Figure 3
<p>Bee plant interactions network (<b>a</b>) in SDTF1 and (<b>b</b>) SDTF2 of Sierra de Quila. Blue lines correspond to Apidae family, red lines to Megachilidae family, yellow lines to Halictidae, green lines to Colletidae, and orange lines to Andrenidae. (SDTF—seasonally dry tropical forest).</p>
Full article ">Figure 4
<p>Bee–plant interactions network (<b>a</b>) in TF<sub>1</sub> and (<b>b</b>) TF<sub>2</sub> of Sierra de Quila. Blue lines correspond to Apidae family, red lines to Megachilidae family, yellow lines to Halictidae, green lines to Colletidae, and orange lines to Andrenidae (TF—temperate forest).</p>
Full article ">
19 pages, 19263 KiB  
Article
Unexpected Genetic Diversity of Nostocales (Cyanobacteria) Isolated from the Phyllosphere of the Laurel Forests in the Canary Islands (Spain)
by Nereida M. Rancel-Rodríguez, Nicole Sausen, Carolina P. Reyes, Antera Martel Quintana, Barbara Melkonian and Michael Melkonian
Microorganisms 2024, 12(12), 2625; https://doi.org/10.3390/microorganisms12122625 - 18 Dec 2024
Viewed by 271
Abstract
A total of 96 strains of Nostocales (Cyanobacteria) were established from the phyllosphere of the laurel forests in the Canary Islands (Spain) and the Azores (Portugal) using enrichment media lacking combined nitrogen. The strains were characterized by light microscopy and SSU rRNA gene [...] Read more.
A total of 96 strains of Nostocales (Cyanobacteria) were established from the phyllosphere of the laurel forests in the Canary Islands (Spain) and the Azores (Portugal) using enrichment media lacking combined nitrogen. The strains were characterized by light microscopy and SSU rRNA gene comparisons. Morphologically, most strains belonged to two different morphotypes, termed “Nostoc-type” and “Tolypothrix-type”. Molecular phylogenetic analysis of 527 SSU rRNA gene sequences of cyanobacteria (95 sequences established during this study plus 392 sequences from Nostocales and 40 sequences from non-heterocyte-forming cyanobacteria retrieved from the databases) revealed that none of the SSU rRNA gene sequences from the phyllosphere of the laurel forests was identical to a database sequence. In addition, the genetic diversity of the isolated strains was high, with 42 different genotypes (44% of the sequences) recognized. Among the new genotypes were also terrestrial members of the genus Nodularia as well as members of the genus Brasilonema. It is concluded that heterocyte-forming cyanobacteria represent a component of the phyllosphere that is still largely undersampled in subtropical/tropical forests. Full article
(This article belongs to the Section Plant Microbe Interactions)
Show Figures

Figure 1

Figure 1
<p>Sampling sites of laurel forests in the Canary Islands and Sao Jorge (the Azores). Numbers refer to sampling sites (localities) in <a href="#microorganisms-12-02625-t001" class="html-table">Table 1</a>.</p>
Full article ">Figure 2
<p>(<b>A</b>–<b>D</b>) Photographic documentation of sampling of leaves and set-up of enrichment cultures. (<b>A</b>) A typical view of the laurel forest of La Gomera (Canary Islands). The tree trunks are heavily colonized by epiphytes. (<b>B</b>) Two sampled leaves of different sizes from <span class="html-italic">Laurus novocanariensis</span>, with their upper surfaces partially covered by epiphylls. (<b>C</b>) Leaf material being prepared for enrichment cultures in a laminar flow hood. (<b>D</b>) Inoculated leaf disks in Petri dishes containing culture media for enrichment of heterocyte-forming cyanobacteria.</p>
Full article ">Figure 3
<p>Overview of PCR and sequencing strategies for cyanobacterial 16S rRNA genes. The position of the primers used for amplification and sequencing of the 16S rRNA gene and the primary and secondary PCR products are shown. The general structure of the ribosomal rDNA operon with the 16S rRNA gene, two tRNA genes, and 23S rDNA gene is depicted schematically at the top of the figure. The primer sequences are shown in <a href="#microorganisms-12-02625-t002" class="html-table">Table 2</a>. Abbreviations used for the primers in the figure refer to the following primer designations and sequences in <a href="#microorganisms-12-02625-t002" class="html-table">Table 2</a>: 16S_SG1_short_forw (SG1), 16S H4_forw (H4-forw), ptLSU C-D_rev (PtL CD R), SG2_rev (SG2), Seq_16S_H4_forw (SeqH4), Seq_16S_1040_rev (1040R), Seq_16S_pos874_forw (874F), and Seq_16S_49_rev (Seq H49R).</p>
Full article ">Figure 4
<p>(<b>A</b>–<b>H</b>) Photographic documentation of the “<span class="html-italic">Nostoc</span>”-type morphotype (L066/CCAC 7008B/BEA 1768B) in a developmental sequence. (<b>A</b>) Several hormogonia (black arrows) characterized by barrel-shaped cells. Scale bar = 10 µm. (<b>B</b>) Differentiated filaments show lenticular to sublenticular vegetative cells (black arrowheads). Spherical to subspherical terminal heterocytes (white arrows) first appear on both ends of a filament, followed by a lenticular to sublenticular intercalary heterocyte (white arrowhead). Scale bar = 10 µm. (<b>C</b>) A common sheath develops surrounding the filament (black arrowhead). Within the sheath, vegetative cells continue to divide, expanding the sheath, with the filament eventually forming a globular structure (black arrow). Scale bar = 10 µm. (<b>D</b>) Terminal heterocytes (white arrows) and the initial intercalary heterocyte (white arrowhead) lack a sheath. Scale bar = 10 µm. (<b>E</b>,<b>F</b>) Curled filaments within expanded sheaths (black arrows) held together by intercalary heterocytes (white arrowheads). Scale bars = 10 µm. (<b>G</b>) When the flexible sheath (black arrowheads) breaks open, hormogonia (black arrows) emerge from the globular structures and start the developmental cycle again. Scale bar = 10 µm. (<b>H</b>) Filaments with intercalary heterocytes (white arrowheads) derived from a broken globular structure. Scale bar = 10 µm.</p>
Full article ">Figure 5
<p>(<b>A</b>–<b>H</b>) Photographic documentation of the “<span class="html-italic">Tolypothrix</span>”-type morphotype (L088/CCAC 7034B/BEA 1790B) in a developmental sequence. (<b>A</b>) Hormogonia are characterized by lenticular to sublenticular cells (black arrow): note the slight polarity of the filament. Scale bar = 10 µm. (<b>B</b>) An older filament with lenticular to sublenticular vegetative cells (black arrowhead) and a spherical to subspherical terminal heterocyte (white arrow). Scale bar = 10 µm. (<b>C</b>) A firm sheath (black arrow) surrounds the straight filament. Early developmental stages of differentiation of intercalary heterocytes from vegetative cells (white arrowheads). Scale bar = 10 µm. (<b>D</b>) Lenticular to sublenticular differentiated intercalary heterocytes (white arrowheads; the left arrowhead depicts two adjacent intercalary heterocytes). The intercalary heterocytes remain enclosed in the firm sheath (unlike the situation in the “<span class="html-italic">Nostoc</span>”-type morphotype). A yellowish firm sheath surrounds vegetative cells of an older filament near a terminal heterocyte (black arrow). Scale bar = 10 µm. (<b>E</b>) Very early stage of the formation of a false branch. A vegetative cell adjacent to an intercalary heterocyte dissociates from the heterocyte and starts to bulge the sheath (black arrow). The intercalary heterocyte of the filament thus becomes a new terminal heterocyte. Scale bar = 10 µm. (<b>F</b>) A false branch attached to a heterocyte (black arrow). Scale bar = 10 µm. (<b>G</b>) Several false branches arising from vegetative cells adjacent to intercalary heterocytes (white arrowheads) or a necrotic cell (white arrow). Scale bar = 20 µm. (<b>H</b>) A primary (black arrow) and a secondary (black arrowhead) false branch share the same firm sheath (white arrowhead). Scale bar = 10 µm.</p>
Full article ">Figure 6
<p>Phylogeny of heterocyte-forming cyanobacteria (Nostocales) from the phyllosphere of the laurel forests in the Canary Islands and the Azores using 16S rDNA sequence comparisons. The split tree (shown in 6 sections) was constructed with a database of 527 sequences, including 95 sequences generated during this study. The 16S rDNA dataset, with 1448 positions, was analyzed with maximum likelihood (RAxML). The model GTR + I + Γ and the parameters were estimated by RAxML (for further details, see <a href="#sec2-microorganisms-12-02625" class="html-sec">Section 2</a>). The sequences generated during this study are highlighted by a grey background and strain numbers (CCAC) in bold (strains with identical sequences are provided with their L numbers as well as the location and plant host in parentheses). Bootstrap values &gt; 50% are shown; the bold value with an asterisk denotes support for the monophyly of the Nostocales. All tree branches in bold received maximal support. The complete merged tree is shown in <a href="#app1-microorganisms-12-02625" class="html-app">Supplementary Figure S1</a>.</p>
Full article ">Figure 6 Cont.
<p>Phylogeny of heterocyte-forming cyanobacteria (Nostocales) from the phyllosphere of the laurel forests in the Canary Islands and the Azores using 16S rDNA sequence comparisons. The split tree (shown in 6 sections) was constructed with a database of 527 sequences, including 95 sequences generated during this study. The 16S rDNA dataset, with 1448 positions, was analyzed with maximum likelihood (RAxML). The model GTR + I + Γ and the parameters were estimated by RAxML (for further details, see <a href="#sec2-microorganisms-12-02625" class="html-sec">Section 2</a>). The sequences generated during this study are highlighted by a grey background and strain numbers (CCAC) in bold (strains with identical sequences are provided with their L numbers as well as the location and plant host in parentheses). Bootstrap values &gt; 50% are shown; the bold value with an asterisk denotes support for the monophyly of the Nostocales. All tree branches in bold received maximal support. The complete merged tree is shown in <a href="#app1-microorganisms-12-02625" class="html-app">Supplementary Figure S1</a>.</p>
Full article ">Figure 6 Cont.
<p>Phylogeny of heterocyte-forming cyanobacteria (Nostocales) from the phyllosphere of the laurel forests in the Canary Islands and the Azores using 16S rDNA sequence comparisons. The split tree (shown in 6 sections) was constructed with a database of 527 sequences, including 95 sequences generated during this study. The 16S rDNA dataset, with 1448 positions, was analyzed with maximum likelihood (RAxML). The model GTR + I + Γ and the parameters were estimated by RAxML (for further details, see <a href="#sec2-microorganisms-12-02625" class="html-sec">Section 2</a>). The sequences generated during this study are highlighted by a grey background and strain numbers (CCAC) in bold (strains with identical sequences are provided with their L numbers as well as the location and plant host in parentheses). Bootstrap values &gt; 50% are shown; the bold value with an asterisk denotes support for the monophyly of the Nostocales. All tree branches in bold received maximal support. The complete merged tree is shown in <a href="#app1-microorganisms-12-02625" class="html-app">Supplementary Figure S1</a>.</p>
Full article ">Figure 6 Cont.
<p>Phylogeny of heterocyte-forming cyanobacteria (Nostocales) from the phyllosphere of the laurel forests in the Canary Islands and the Azores using 16S rDNA sequence comparisons. The split tree (shown in 6 sections) was constructed with a database of 527 sequences, including 95 sequences generated during this study. The 16S rDNA dataset, with 1448 positions, was analyzed with maximum likelihood (RAxML). The model GTR + I + Γ and the parameters were estimated by RAxML (for further details, see <a href="#sec2-microorganisms-12-02625" class="html-sec">Section 2</a>). The sequences generated during this study are highlighted by a grey background and strain numbers (CCAC) in bold (strains with identical sequences are provided with their L numbers as well as the location and plant host in parentheses). Bootstrap values &gt; 50% are shown; the bold value with an asterisk denotes support for the monophyly of the Nostocales. All tree branches in bold received maximal support. The complete merged tree is shown in <a href="#app1-microorganisms-12-02625" class="html-app">Supplementary Figure S1</a>.</p>
Full article ">Figure 6 Cont.
<p>Phylogeny of heterocyte-forming cyanobacteria (Nostocales) from the phyllosphere of the laurel forests in the Canary Islands and the Azores using 16S rDNA sequence comparisons. The split tree (shown in 6 sections) was constructed with a database of 527 sequences, including 95 sequences generated during this study. The 16S rDNA dataset, with 1448 positions, was analyzed with maximum likelihood (RAxML). The model GTR + I + Γ and the parameters were estimated by RAxML (for further details, see <a href="#sec2-microorganisms-12-02625" class="html-sec">Section 2</a>). The sequences generated during this study are highlighted by a grey background and strain numbers (CCAC) in bold (strains with identical sequences are provided with their L numbers as well as the location and plant host in parentheses). Bootstrap values &gt; 50% are shown; the bold value with an asterisk denotes support for the monophyly of the Nostocales. All tree branches in bold received maximal support. The complete merged tree is shown in <a href="#app1-microorganisms-12-02625" class="html-app">Supplementary Figure S1</a>.</p>
Full article ">
9 pages, 666 KiB  
Brief Report
Low Mortality Rates Among Tropical Ferns
by Laura Salazar, Jürgen Kluge, Jürgen Homeier and Michael Kessler
Int. J. Plant Biol. 2024, 15(4), 1360-1368; https://doi.org/10.3390/ijpb15040094 - 18 Dec 2024
Viewed by 212
Abstract
Tropical ferns are underrepresented in demographic studies, despite their ecological importance in forest ecosystems. This study investigates the mortality rates of terrestrial ferns along an elevational gradient (500–4000 m a.s.l.) in Ecuador, focusing on relationships with environmental variables, community characteristics, and plant size. [...] Read more.
Tropical ferns are underrepresented in demographic studies, despite their ecological importance in forest ecosystems. This study investigates the mortality rates of terrestrial ferns along an elevational gradient (500–4000 m a.s.l.) in Ecuador, focusing on relationships with environmental variables, community characteristics, and plant size. Over two years (2009–2011), 3213 individuals representing 88 species were monitored in 22 permanent plots across eight elevations. Mortality rates, calculated as the percentage of individuals lost annually, averaged 0.87%, with a hump-shaped trend along the gradient and a significant negative relationship with temperature. Mortality rates were positively correlated with species richness and fern density, suggesting competition may influence community structure. Larger individuals exhibited higher mortality rates, likely due to greater resource demands and exposure to environmental stressors. These findings emphasize the interplay of abiotic factors, such as elevation and temperature, and biotic interactions, including competition and herbivory, in shaping fern population dynamics. The low mortality rates observed reflect population stability, potentially linked to unique life history traits, such as extended generation times. This study provides critical insights into the demographic strategies of tropical ferns and underscores the need for long-term research to better understand their responses to environmental and biotic pressures. Full article
(This article belongs to the Section Plant Ecology and Biodiversity)
Show Figures

Figure 1

Figure 1
<p>Relationship between mortality rate (%) of ferns and (<b>a</b>) elevation (m a.s.l.) and (<b>b</b>) temperature (°C), both modeled using second-degree polynomial regression. In both panels, the dots represent the percentage of mortality observed at different elevations. The dashed line in panel (<b>a</b>) indicates a non-significant trend, while the black line in panel (<b>b</b>) shows a significant relationship, with the equation and R<sup>2</sup> value displayed. The asterisks next to the R<sup>2</sup> value denote the level of statistical significance: * moderately significant (<span class="html-italic">p</span> ≤ 0.05).</p>
Full article ">Figure 2
<p>Relationships between (<b>a</b>) mortality rate (%) and species richness of ferns, (<b>b</b>) mortality rate (%) and number of individuals of ferns, and (<b>c</b>) species richness and number of individuals of ferns. The respective equations and R<sup>2</sup> values are displayed within each panel. In panels (<b>a</b>,<b>b</b>), the dots represent the percentage of mortality at specific numbers of species (<b>a</b>) or individuals (<b>b</b>). In panel (<b>c</b>), the dots represent the mean species richness and number of individuals per elevation. Only seven data points are visible in panel (<b>b</b>) due to overlapping values at different elevations. The asterisks next to the R<sup>2</sup> value denote the level of statistical significance: ** significant (<span class="html-italic">p</span> ≤ 0.01), * moderately significant (<span class="html-italic">p</span> ≤ 0.05).</p>
Full article ">Figure 3
<p>Mortality rate (%) of ferns by size class (cm) for 2009–2010 (darker bars) and 2010–2011 (lighter bars), categorized by leaf length: 10–30 cm, 30–50 cm, 50–70 cm, 70–100 cm, and &gt;100 cm.</p>
Full article ">
16 pages, 3229 KiB  
Article
Analysis of CH4 and N2O Fluxes in the Dry Season: Influence of Soils and Vegetation Types in the Pantanal
by Gabriela Cugler, Viviane Figueiredo, Vincent Gauci, Tainá Stauffer, Roberta Bittencourt Peixoto, Sunitha Rao Pangala and Alex Enrich-Prast
Forests 2024, 15(12), 2224; https://doi.org/10.3390/f15122224 - 17 Dec 2024
Viewed by 233
Abstract
This study examines CH4 and N2O fluxes during the dry season in two distinct areas of the Pantanal: Barranco Alto Farm (BAF), dominated by grasslands, and Passo da Lontra (PL), a forested region. As climate change increases the occurrence of [...] Read more.
This study examines CH4 and N2O fluxes during the dry season in two distinct areas of the Pantanal: Barranco Alto Farm (BAF), dominated by grasslands, and Passo da Lontra (PL), a forested region. As climate change increases the occurrence of droughts, understanding greenhouse gas (GHG) fluxes in tropical wetlands during dry periods is crucial. Using static chambers, CH4 and N2O emissions were measured from soils and tree stems in both regions, with additional measurements from grass in BAF. Contrary to expectations, PL—characterized by clayey soils—had sandy mud samples that retained less water, promoting oxic conditions and methane uptake, making it a CH4 sink. Meanwhile, BAF’s sandy, well-drained soils exhibited minimal CH4 fluxes, with negligible methane uptake or emissions. N2O fluxes were generally higher in BAF, particularly from tree stems, indicating significant interactions between soil type, moisture, and vegetation. These findings highlight the pivotal roles of soil texture and aeration in GHG emissions, suggesting that well-drained, sandy soils in tropical wetlands may not always enhance methane oxidation. This underscores the importance of continuous GHG monitoring in the Pantanal to refine climate change mitigation strategies. Full article
(This article belongs to the Section Forest Meteorology and Climate Change)
Show Figures

Figure 1

Figure 1
<p>Location of Pantanal sampling sites. (<b>A</b>) The top-left map highlights the Pantanal biome (grey) within Brazil’s borders. (<b>B</b>) A zoomed-in view of the southern Pantanal shows the sampling sites: Passo da Lontra (PL, triangle) in the Miranda microregion and Barranco Alto Farm (BAF, circle) in the Aquidauana microregion. (<b>C</b>) A detailed map of the PL site near Medalha Lake and the Rio Miranda. (<b>D</b>) A detailed map of the BAF site near the Aquidauana River, with surrounding water bodies in light blue. The shapefiles for the Pantanal boundaries and hydrography were obtained from Terrabrasilis (INPE, 2023), while the map of Brazil and municipality boundaries were sourced from IBGE (2023).</p>
Full article ">Figure 2
<p>Photographs showing the chambers used to measure CH<sub>4</sub> and N<sub>2</sub>O fluxes at Fazenda Barranco Alto and Passo do Lontra. Opaque PVC static chambers were used for measuring fluxes from grass and soil, while semi-rigid static chambers were used for tree stem measurements. Source: Photographs are taken by collaborators Pernilha Eriksson and Louise Larsson and are the property of the research group.</p>
Full article ">Figure 3
<p>Box plot illustrating CH<sub>4</sub> fluxes (µg C-CH<sub>4</sub> m<sup>−2</sup> d<sup>−1</sup>) measured across compartments and sites. The BAF site includes CH<sub>4</sub> emissions from tree stems, soil, and grass, while the PL site includes emissions from tree stems and soil. Each box represents the interquartile range (IQR), with whiskers extending to the minimum and maximum values, including the outliers (black circles). The Kolmogorov–Smirnov test indicates that the distribution of all data is nonparametric (<span class="html-italic">p</span> &lt; 0.05). Different letters represent statistically significant differences according to Kruskal–Wallis test with Dunn’s post hoc test (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 4
<p>Box plot illustrating N<sub>2</sub>O fluxes (µg N-N<sub>2</sub>O m<sup>−2</sup> d<sup>−1</sup>) measured from tree steams, exposed soil, and grasses across PL and BAF study sites. The BAF site includes N<sub>2</sub>O emissions from tree stems, soil, and grass, while the PL site includes emissions from tree stems and soil. Each box represents the interquartile range (IQR), with whiskers extending to the minimum and maximum values, including the outliers (black circles). Letter (a) above the boxes represents no statistically significant differences according to the Kruskal–Wallis test with Dunn’s post hoc test (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 5
<p>Boxplots illustrating CH<sub>4</sub> and N<sub>2</sub>O fluxes at Passo da Lontra (PL) and Barranco Alto Farm (BAF) across three areas (Area 1: closest to the lake, Area 3: furthest). Panels (<b>A</b>,<b>B</b>) depict CH<sub>4</sub> fluxes, while panels (<b>C</b>,<b>D</b>) show N<sub>2</sub>O fluxes. Each box represents the interquartile range (IQR), with whiskers extending to minimum and maximum non-outlier values. The letter (a) above the boxes represents no statistically significant differences according to the Kruskal–Wallis test with Dunn’s post hoc test (<span class="html-italic">p</span> &lt; 0.05).</p>
Full article ">Figure 6
<p>Relationship between tree stem diameter (cm) and GHG fluxes. (<b>A</b>) Represent the CH<sub>4</sub> (μg CH<sub>4</sub> m<sup>−2</sup> d<sup>−1</sup>). (<b>B</b>) Represent the N<sub>2</sub>O (μg N<sub>2</sub>O m<sup>−2</sup> d<sup>−1</sup>). The blue lines show the non-parametric trend (LOWESS) of fluxes with increasing stem diameter.</p>
Full article ">
30 pages, 9613 KiB  
Article
Mapping Soil Properties in Tropical Rainforest Regions Using Integrated UAV-Based Hyperspectral Images and LiDAR Points
by Yiqing Chen, Tiezhu Shi, Qipei Li, Chao Yang, Zhensheng Wang, Zongzhu Chen and Xiaoyan Pan
Forests 2024, 15(12), 2222; https://doi.org/10.3390/f15122222 - 17 Dec 2024
Viewed by 244
Abstract
For tropical rainforest regions with dense vegetation cover, the development of effective large-scale soil mapping methods is crucial to improve soil management practices to replace the time-consuming and laborious conventional approaches. While machine learning (ML) algorithms demonstrate superior predictability of soil properties over [...] Read more.
For tropical rainforest regions with dense vegetation cover, the development of effective large-scale soil mapping methods is crucial to improve soil management practices to replace the time-consuming and laborious conventional approaches. While machine learning (ML) algorithms demonstrate superior predictability of soil properties over linear models, their practical and automated application for predicting soil properties using remote sensing data requires further assessment. Therefore, this study aims to integrate Unmanned Aerial Vehicles (UAVs)-based hyperspectral images and Light Detection and Ranging (LiDAR) points to predict the soil properties indirectly in two tropical rainforest mountains (Diaoluo and Limu) in Hainan Province, China. A total of 175 features, including texture features, vegetation indices, and forest parameters, were extracted from two study sites. Six ML models, Partial Least Squares Regression (PLSR), Random Forest (RF), Adaptive Boosting (AdaBoost), Gradient Boosting Decision Trees (GBDT), Extreme Gradient Boosting (XGBoost), and Multilayer Perceptron (MLP), were constructed to predict soil properties, including soil acidity (pH), total nitrogen (TN), soil organic carbon (SOC), and total phosphorus (TP). To enhance model performance, a Bayesian optimization algorithm (BOA) was introduced to obtain optimal model hyperparameters. The results showed that compared with the default parameter tuning method, BOA always improved models’ performances in predicting soil properties, achieving average R2 improvements of 202.93%, 121.48%, 8.90%, and 38.41% for soil pH, SOC, TN, and TP, respectively. In general, BOA effectively determined the complex interactions between hyperparameters and prediction features, leading to an improved model performance of ML methods compared to default parameter tuning models. The GBDT model generally outperformed other ML methods in predicting the soil pH and TN, while the XGBoost model achieved the highest prediction accuracy for SOC and TP. The fusion of hyperspectral images and LiDAR data resulted in better prediction of soil properties compared to using each single data source. The models utilizing the integration of features derived from hyperspectral images and LiDAR data outperformed those relying on one single data source. In summary, this study highlights the promising combination of UAV-based hyperspectral images with LiDAR data points to advance digital soil property mapping in forested areas, achieving large-scale soil management and monitoring. Full article
(This article belongs to the Section Forest Inventory, Modeling and Remote Sensing)
Show Figures

Figure 1

Figure 1
<p>Workflow of the soil property mapping method in tropical rainforest regions.</p>
Full article ">Figure 2
<p>(<b>a</b>) Geographic location of Hainan Province, China; spatial distribution of soil samples in (<b>b</b>) Diaoluo, and (<b>c</b>) Limu mountain.</p>
Full article ">Figure 3
<p>Top and side 3D view of LiDAR point cloud of (<b>a</b>) Diaoluo and (<b>b</b>) Limu mountains.</p>
Full article ">Figure 4
<p>Comparison of soil properties between samples from Diaoluo and Limu mountains: (<b>a</b>) pH; (<b>b</b>) soil organic carbon (SOC); (<b>c</b>) total nitrogen (TN); and (<b>d</b>) total phosphorus (TP). Dashed lines represent the mean value.</p>
Full article ">Figure 4 Cont.
<p>Comparison of soil properties between samples from Diaoluo and Limu mountains: (<b>a</b>) pH; (<b>b</b>) soil organic carbon (SOC); (<b>c</b>) total nitrogen (TN); and (<b>d</b>) total phosphorus (TP). Dashed lines represent the mean value.</p>
Full article ">Figure 5
<p>Importance ranking of the 15 selected features for predicting the (<b>a</b>) pH, (<b>b</b>) soil organic carbon (SOC), (<b>c</b>) total nitrogen (TN), and (<b>d</b>) total phosphorus (TP).</p>
Full article ">Figure 6
<p>Scatter plots of the measured values against soil property levels predicted by the optimal models: (<b>a</b>) pH predicted by the GBDT model; (<b>b</b>) soil organic carbon (SOC) predicted by the XGBoost model; (<b>c</b>) total nitrogen (TN) predicted by the GBDT model; (<b>d</b>) total phosphorus (TP) predicted by the XGBoost model.</p>
Full article ">Figure 7
<p>Spatial distributions of the soil properties, including pH, soil organic carbon (SOC), total nitrogen (TN), and total phosphorus (TP), in (<b>a</b>) Diaoluo and (<b>b</b>) Limu mountains.</p>
Full article ">Figure 7 Cont.
<p>Spatial distributions of the soil properties, including pH, soil organic carbon (SOC), total nitrogen (TN), and total phosphorus (TP), in (<b>a</b>) Diaoluo and (<b>b</b>) Limu mountains.</p>
Full article ">
16 pages, 3298 KiB  
Article
Identification of Chemical Constituents from Leaves and Stems of Alpinia oxyphylla: Potential Antioxidant and Tyrosinase Inhibitory Properties
by Huiqin Chen, Xin Su, Pan Xiang, Yanmei Wei, Hao Wang, Juntao Li, Shoubai Liu, Wenli Mei and Haofu Dai
Antioxidants 2024, 13(12), 1538; https://doi.org/10.3390/antiox13121538 - 16 Dec 2024
Viewed by 332
Abstract
Alpinia oxyphylla Miq. is an important undergrowth species in southern China. The fruits of A. oxyphylla are recognized as one of “the four famous south medicines” and are also used in the production of preserved fruit. However, as non-medicinal parts, their stems and [...] Read more.
Alpinia oxyphylla Miq. is an important undergrowth species in southern China. The fruits of A. oxyphylla are recognized as one of “the four famous south medicines” and are also used in the production of preserved fruit. However, as non-medicinal parts, their stems and leaves are unutilized. In order to promote resource recycling, the chemical components of such stems and leaves were investigated, and we evaluated their melanin inhibitory potential through DPPH and ABTS radical scavenging, tyrosinase inhibition, and melanin production inhibition in B16 cells. Five new compounds, aloxy A (1), kaempferol 3-O-α-L-rhamnosyl-(1 → 2)-(3″,4″-diacetyl-β-D-glucuronate methyl ester) (2), quercetin 3-O-α-L-rhamnosyl-(1 → 2)-(3″,4″-diacetyl-β-D-glucuronate methyl ester) (3), kaempferol 3-O-α-L-rhamnosyl-(1 → 3)-(4″-acetyl-β-D-glucuronate methyl ester) (4), and kaempferol 3-O-α-L-rhamnosyl-(1 → 2)-(3″-acetyl-β-D-glucuronate methyl ester) (5), and seventeen known ones (622) were isolated and identified from the stems and leaves of A. oxyphylla. Among these compounds, 19 compounds presented tyrosinase inhibitory activities, among which aloxy A (1), hexahydrocurcumin (7), gingerenone A (8) and 4,4′-dimethoxy-3′-hydroxy-7,9′:7′,9-diepoxylignan-3-O-β-D-glucopyranoside (22) showed strong inhibitory activity, with IC50 values between 6.26 ± 0.42 and 22.04 ± 1.09 μM, lower than the positive control (Kojic acid, IC50 = 37.22 ± 1.64 μM). A total of 15 compounds exhibited varying degrees of DPPH and ABTS radical scavenging activities. In addition, 1, 2, and 7 showed melanin production inhibition activity in B16 cells, and the effects presented as concentration-dependent. The above results indicate that the stems and leaves of A. oxyphylla are rich with phenolic compounds, and display tyrosinase inhibition and antioxidant activities, which could lead to potential applications related to melanin production inhibition such as in the development of cosmetics. Full article
(This article belongs to the Section Natural and Synthetic Antioxidants)
Show Figures

Figure 1

Figure 1
<p>Isolation process of 5 new compounds.</p>
Full article ">Figure 2
<p>Structures of isolated compounds.</p>
Full article ">Figure 3
<p>The key <sup>1</sup>H-<sup>1</sup>H COSY, HMBC, and ROESY correlations of compound <b>1</b>.</p>
Full article ">Figure 4
<p>The key <sup>1</sup>H-<sup>1</sup>H COSY, HMBC, and ROESY correlations of compounds <b>2</b>–<b>5</b>.</p>
Full article ">Figure 5
<p>Single-crystal X-ray diffractometry of <b>2</b>.</p>
Full article ">Figure 6
<p>HOMO distribution of compounds <b>2</b>, <b>9</b>, <b>12</b>, <b>6</b>–<b>8</b>, and <b>19</b>–<b>21</b> in ethanol.</p>
Full article ">Figure 7
<p>Melanin inhibitory activity of compounds <b>1</b>, <b>2</b>, and <b>7</b> in B16 cells. Each column represents means ± SD of three independent experiments. * <span class="html-italic">p</span> &lt; 0.05, ** <span class="html-italic">p</span> &lt; 0.01 indicate significant difference from positive control (kojic acid).</p>
Full article ">
29 pages, 3186 KiB  
Article
Pollen Rain in a Semi-Arid Area of Northeastern Brazil: Pollen Diversity, Concentrations over Two Years and Their Relationship with Ecological Aspects
by Francisco Hilder Magalhães-e-Silva and Francisco de Assis Ribeiro dos Santos
Aerobiology 2024, 2(4), 118-146; https://doi.org/10.3390/aerobiology2040009 - 13 Dec 2024
Viewed by 343
Abstract
Pollen rain studies are rare in arid and semi-arid regions worldwide. Interpretations related to the dynamics of plant communities and possible paleoclimatic changes in these areas face significant limitations due to this lack of data. The global biome of Seasonally Dry Tropical Forests [...] Read more.
Pollen rain studies are rare in arid and semi-arid regions worldwide. Interpretations related to the dynamics of plant communities and possible paleoclimatic changes in these areas face significant limitations due to this lack of data. The global biome of Seasonally Dry Tropical Forests and Shrublands (SDTFS) is represented in Northeast Brazil by the caatinga, which is composed of xerophytic vegetation. This study aimed to generate information about the pollen rain in this area and to understand its relationship with species flowering, pollination syndromes, life forms, and climatic aspects. A caatinga area in Canudos, Bahia, Brazil (09°54′ S 39°07′ W), was selected for this purpose. Artificial pollen collectors were installed and exchanged monthly over two years for palynological analyses of the collected material, using standard palynological techniques. A total of 124 pollen types were identified, with approximately 8823 pollen grains deposited per cm2 over the two years. Several vegetation components were represented in the pollen rain, reflecting local plant diversity, life forms, and physiognomies. A positive relationship was observed between increased temperature and pollen production from trees and shrubs, and new pollen types were associated with indicator species of caatinga vegetation. Full article
Show Figures

Figure 1

Figure 1
<p>Location of the Canudos Biological Station (CBS), Bahia, semi-arid of Brazil.</p>
Full article ">Figure 2
<p>The general aspect of the landscape and vegetation of the CBS, Bahia, semi-arid of Brazil, in the rainy season in February 2005. Valley point (VP) and hill point (HP) show where pollen Tauber collectors were placed.</p>
Full article ">Figure 3
<p>Monthly averages of maximum temperatures (°C) recorded for the CBS (Canudos, Bahia, Brazil) during the study period (March 2003 to February 2005). Top line: averages of the maximum temperatures; middle line: average of the mean temperatures; and bottom line: average of the minimum temperatures.</p>
Full article ">Figure 4
<p>Monthly average rainfall (mm) recorded for the CBS (Canudos, Bahia, Brazil) during the study period (March 2003 to February 2005), Canudos, Bahia.</p>
Full article ">Figure 5
<p>Percentages of pollen types in the annual concentrations of pollen rain in the CBS (Canudos, Bahia, Brazil) according to pollination syndromes of related species.</p>
Full article ">Figure 6
<p>Percentages of pollen types in the annual concentrations of pollen rain in the CBS (Canudos, Bahia, Brazil) according to pollination syndromes of related families.</p>
Full article ">Figure 7
<p>Percentages of pollen types in the annual concentrations of pollen rain in the CBS (Canudos, Bahia, Brazil) according to the pollination of the respective species related to them.</p>
Full article ">Figure 8
<p>Percentages of pollen types in the annual concentrations of pollen rain in the CBS (Canudos, Bahia, Brazil) according to life forms of related species.</p>
Full article ">
20 pages, 2762 KiB  
Article
Potential Reductions in Carbon Emissions from Indonesian Forest Concessions Through Use of Reduced-Impact Logging Practices
by Hermudananto, Ethan P. Belair, Hasbie Hasbillah, Peter W. Ellis, Ruslandi and Francis E. Putz
Forests 2024, 15(12), 2198; https://doi.org/10.3390/f15122198 - 13 Dec 2024
Viewed by 309
Abstract
To estimate the potential and realized carbon emission reductions from implementation of reduced-impact logging (RIL) in Indonesia, we compiled logging emissions data from 15 concessions in Kalimantan and 10 from the Papuan provinces. Committed emissions data were collected for harvested timber as well [...] Read more.
To estimate the potential and realized carbon emission reductions from implementation of reduced-impact logging (RIL) in Indonesia, we compiled logging emissions data from 15 concessions in Kalimantan and 10 from the Papuan provinces. Committed emissions data were collected for harvested timber as well as from collateral damage caused by felling, skidding, and clearing for haul roads and log yards. Emissions expressed as mean ± standard error per cubic meter of timber harvested, per area harvested, and per Mg of timber harvested (i.e., the ‘Carbon Impact Factor’) were 1.30 ± 0.15 Mg C m−3, 27.52 ± 4.44 Mg C ha−1, and 6.88 ± 0.84 Mg Mg−1, respectively. Among the sampled concessions, felling, hauling, and skidding caused 18–86%, 2–48%, and 6–75% of these emissions, respectively. Potential emission reductions calculated as the difference between observed emissions and those of the five best-performing concessions are 0.67 ± 0.15 Mg C m−3, 21.11 ± 4.38 Mg C ha−1, and 4.20 ± 0.83 Mg Mg−1, which represents reductions of 51%, 76%, and 61%, respectively. Extrapolating these estimates to all of Indonesia using average log production data from 2018 to 2021 results in an estimated annual emissions reduction of 14.47 Tg CO2 from full adoption of RIL, which is 2.9% of Indonesia’s nationally determined contribution (NDC) from the forestry sector. Full article
Show Figures

Figure 1

Figure 1
<p>The 25 Indonesian natural forest management concessions sampled, 15 in Kalimantan and 10 in the Papuan provinces (FSC-certified concessions are circled).</p>
Full article ">Figure 2
<p>Carbon emissions per cubic meter of wood harvested (Mg C m<sup>−3</sup>; <b>top panel</b>), per area harvested (Mg C ha<sup>−1</sup>; <b>middle panel</b>), or as the CIF (Mg Mg<sup>−1</sup>; <b>bottom panel</b>). Emissions are given for felled tree remainders, felling collateral damage, skidding, haul roads, and log yards. Mean harvest intensities (m<sup>3</sup> ha<sup>−1</sup>) are noted on top of each bar. All concessions except Concession S have log-yard emissions, but some are not obvious on the graphs due to very low values. FSC-certified concessions are circled; an asterisk above the bar indicates that there was evidence of previous logging in the sampled block.</p>
Full article ">Figure 3
<p>Emissions of above- and below-ground biomass carbon from trees &gt; 10 cm DBH, with observed selective logging practices and modeled emission reductions from implementing RIL-C procedures (green bars; average of the five best-performing concessions) in Kalimantan, Papua, and at the country level per cubic meter of wood harvested (Mg C m<sup>−3</sup>; <b>top panel</b>), per area harvested (Mg C ha<sup>−1</sup>; <b>middle panel</b>), or as the CIF (Mg Mg<sup>−1</sup>; <b>bottom panel</b>).</p>
Full article ">Figure 4
<p>Effects of harvest intensity expressed as m<sup>3</sup> ha<sup>−1</sup> (upper three panels) and as number of trees harvested ha<sup>−1</sup> (lower three panels) on logging emissions per m<sup>3</sup> of extracted timber (<b>left</b>), as Mg C ha<sup>−1</sup> (<b>center</b>), and as the CIF (<b>right</b>). The drawn lines visualize the trends through the moving central tendency of the committed emissions-harvest intensity relationships (FSC-certified concessions circled; blue for Kalimantan, red for Papua). An asterisk adjacent to the alphabetic concession code indicates that there was evidence of previous industrial logging in the sampled block.</p>
Full article ">Figure 5
<p>Comparisons of mean carbon emissions (Mg C) from skid trails and haul road construction per m<sup>3</sup> of extracted timber (<b>left</b>), as Mg C ha<sup>−1</sup> (<b>center</b>), and as the CIF (<b>right</b>). FSC-certified concessions are circled: blue for Kalimantan and red for Papua. An asterisk adjacent to the alphabetic concession code indicates that there was evidence of previous industrial logging in the sampled block.</p>
Full article ">
19 pages, 1943 KiB  
Article
An International Perspective on the Status of Wildlife in Türkiye’s Sustainable Forest Management Processes
by Çağdan Uyar, Dalia Perkumienė, Mindaugas Škėma and Marius Aleinikovas
Forests 2024, 15(12), 2195; https://doi.org/10.3390/f15122195 - 12 Dec 2024
Viewed by 534
Abstract
Ensuring the sustainability of forests is among the priority measures to be taken against the decline in biodiversity, which is among the world’s increasingly common concerns. This study investigated whether sustainable forest management processes are considering wildlife conservation objectives. Ten forest management processes [...] Read more.
Ensuring the sustainability of forests is among the priority measures to be taken against the decline in biodiversity, which is among the world’s increasingly common concerns. This study investigated whether sustainable forest management processes are considering wildlife conservation objectives. Ten forest management processes were categorized and then analyzed for whether wildlife conservation is adequately considered. The wildlife data were grouped into four categories, with the most common being the protection of biodiversity and wildlife trade. The satisfaction level obtained according to the scoring method used was determined as the criterion of success in wildlife conservation. According to the scoring method applied, the overall success was found to be 50%. It was determined that a standard should be developed regarding the economic value of wildlife fauna and flora species and that this issue should be included in sustainable forest management strategies. Only 20 of 116 total sustainable forest management criteria considered wildlife. The African Timber Organization process, which has the most member countries, was identified as the process with the lowest number of wildlife criteria, at 2%, while the International Tropical Timber Organization process was found to have the most wildlife protection criteria at 20%. The conservation success rates for the two processes of which Türkiye is a member were also found to be quite low. It is concluded that there is a need to strengthen the place of wildlife, one of the most important living components for forests, in SFM processes both for Türkiye and internationally. The results obtained were evaluated both in terms of international criteria and practices in Türkiye. It is also recommended that future international meetings include wildlife health and diversity as a separate criterion when determining sustainable methods. Full article
(This article belongs to the Special Issue Wildlife Ecology and Conservation in Forest Habitats)
Show Figures

Figure 1

Figure 1
<p>Criteria counts for wildlife in SFM processes.</p>
Full article ">Figure 2
<p>Percentage of criteria for wildlife sustainability.</p>
Full article ">Figure 3
<p>Criteria counts pertaining to wildlife protection.</p>
Full article ">
16 pages, 3435 KiB  
Article
Ultrasound Corrosion Mapping on Hot Stainless Steel Surfaces
by Jan Lean Tai, Mohamed Thariq Hameed Sultan, Farah Syazwani Shahar, Andrzej Łukaszewicz, Zbigniew Oksiuta and Rafał Grzejda
Metals 2024, 14(12), 1425; https://doi.org/10.3390/met14121425 - 12 Dec 2024
Viewed by 404
Abstract
This study investigates the application of Phased Array Corrosion Mapping (PACM) as a non-destructive testing (NDT) method for detecting and monitoring corrosion growth on hot stainless steel (SS) surfaces, specifically focusing on SS 304 and SS 316. Conducted across a temperature range of [...] Read more.
This study investigates the application of Phased Array Corrosion Mapping (PACM) as a non-destructive testing (NDT) method for detecting and monitoring corrosion growth on hot stainless steel (SS) surfaces, specifically focusing on SS 304 and SS 316. Conducted across a temperature range of 30 °C to 250 °C, the research evaluates the effectiveness of PACM in high-temperature environments typical of the petrochemical industry. Experiments were conducted using specimens with machined slots and flat-bottom holes (FBHs) to simulate corrosion defects. The results demonstrate that PACM effectively detects and maps corrosion indicators, with color-coded C-scan data facilitating easy interpretation. Temperature variations significantly influenced ultrasound signal characteristics, leading to observable changes in FBH indications, particularly at elevated temperatures. Increased ultrasound attenuation necessitated adjustments in decibel settings to maintain accuracy. SS 304 and SS 316 exhibited distinct responses to temperature changes, with SS 316 showing higher dB values and unique signal behaviors, including increased scattering and noise echoes at elevated temperatures. Detected depths for slots and FBHs correlated closely with designed depths, with deviations generally less than 0.5 mm; however, some instances showed deviations exceeding 2 mm, underscoring the need for careful interpretation. At temperatures above 230 °C, the disbanding of probe elements led to weak or absent signals, complicating data interpretation and requiring adjustments in testing protocols. This study highlights the feasibility and effectiveness of PACM for corrosion detection on hot SS surfaces, providing critical insights into material behavior under thermal conditions. Future research should include physical examination of samples using Scanning Electron Microscopy (SEM) to validate and enhance the reliability of the findings. The integration of non-contact NDT methods and optimization of calibration techniques are essential for improving PACM performance at elevated temperatures. Full article
(This article belongs to the Section Corrosion and Protection)
Show Figures

Figure 1

Figure 1
<p>Schematic of the test specimen design with identification number.</p>
Full article ">Figure 2
<p>(<b>a</b>) Corrosion mapping data for SS 304 at 30 °C; (<b>b</b>) 100 °C; (<b>c</b>) 110 °C; (<b>d</b>) 200 °C; (<b>e</b>) 230 °C; (<b>f</b>) 250 °C.</p>
Full article ">Figure 3
<p>(<b>a</b>) Corrosion mapping data for SS 316 at 30 °C; (<b>b</b>) 100 °C; (<b>c</b>) 190 °C; (<b>d</b>) 210 °C; (<b>e</b>) 230 °C; (<b>f</b>) 250 °C.</p>
Full article ">Figure 3 Cont.
<p>(<b>a</b>) Corrosion mapping data for SS 316 at 30 °C; (<b>b</b>) 100 °C; (<b>c</b>) 190 °C; (<b>d</b>) 210 °C; (<b>e</b>) 230 °C; (<b>f</b>) 250 °C.</p>
Full article ">Figure 4
<p>Indication dimension measurement.</p>
Full article ">
Back to TopTop