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331 results for “plantation”
FIGURE 14 in A new species of Paropsisterna Motschulsky, 1860, a significant pest of plantation eucalypts in Tasmania and Ireland (Coleoptera: Chrysomelidae: Chrysomelinae)
FIGURE 14. Third instar larva of Paropsisterna selmani, new species.
Fig. 1 in First Report ofHeilipodus dorsosulcatus(Boheman, 1843) (Coleoptera: Curculionidae) in a Plantation ofEucalyptusL'Héritier in Brazil
Fig. 1. Damage (arrows) by Heilipodus dorsosulcatus in young plantations of Eucalyptus.
Effects of transformation of inefficient Camellia oleifera plantation on soil quality and fungal community(supplementary)
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Fig. 2 in Effects Of Leaf-Litter Addition On Carabid Beetles In A Non-Native Norway Spruce Plantation
Fig. 2. The mean numbers (± S. E.) of the five dominant carabid species in the control and leaf-litter plots. Note different scales in the vertical axes
Fig. 3 in Taxonomic Structure Of Nematode Communities Of Epiphytic Mosses In Green Plantations Of Chernihiv, Ukraine
Fig. 3. Structure of nematode communities of epiphytic mosses in green plantations of Chernihiv according to the dominance criterion.
Seed rain and soil seed banks in Chinese fir plantations and an adjacent natural forest
<p>The natural regeneration of native broadleaved species underneath forest monoculture plantations is important to recover ecosystem functions and to mitigate adverse environmental effects. To understand how seed rain and soil seed banks facilitate natural regeneration, we surveyed their density and composition in a monoculture Chinese fir plantation, a mixed Chinese fir–broadleaf plantation, and an adjacent natural broadleaved forest for two years in southern China. Twenty-eight species (16 families) were in seed rain, and 45 species (27 families) were in soil seed banks. Seed rain density did not differ significantly across stands; however, the number of taxa in seed rain was highest in the mixed plantation and lowest in the natural forest. Seed bank density was significantly higher in the mixed plantation than in the other stands. The Sørensen similarity indices of species composition between seed sources and aboveground vegetation were relatively low (<0.50). In addition, the seeds of native tree species common to the seed banks of the three forests indicated the adjacent natural forest was a seed source for the natural regeneration of native species in forest plantations. To augment regeneration and accelerate the rate of conversion, we recommend direct seeding or planting of desired species.</p>
Data for "Cost-effectiveness of natural forest regeneration and plantations for climate mitigation"
<p>All data associated with Busch et al. (2024) “Cost-effectiveness of natural forest regeneration and plantations for climate mitigation,” <em>Nature Climate Change</em>, doi: 10.1038/s41558-024-02068-1 are publicly available here. To facilitate reproducibility of our results and use of our datasets, we provide all intermediate datasets in addition to the final results. We provide brief dsecriptions of the published datasets in the 00_README.docx file, including contact information for individuals associated with each dataset. We encourage the use of our data and are happy to answer questions as needed.</p> <p>When using these data, please cite:</p> <p>Busch, J., Bukoski, J.J., Cook-Patton, S.C. Griscom, B., Kaczan, D., Potts, M.D., Yi, Y., and Vincent, J.R. Cost-effectiveness of natural forest regeneration and plantations for climate mitigation. <em>Nat. Clim. Chang.</em> <strong>14</strong>, 996–1002 (2024). https://doi.org/10.1038/s41558-024-02068-1</p>
Presence points of infested trees by Xyleutes ceramica in 10 teak plantations in Thailand
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Dataset for "Optimistic growth of marginal region plantations under climate warming: assessing divergent drought resilience"
<p>Dataset for published paper "<em>Optimistic growth of marginal region plantations under climate warming: assessing divergent drought resilience</em>", including the original tree-ring for four species and site features (topographic information, soil conditions, and LIDAR extracted data).</p>
Figure 6 from: Pham NQ, Barnes I, Chen S, Pham TQ, Lombard L, Crous PW, Wingfield MJ (2018) New species of Cylindrocladiella from plantation soils in South-East Asia. MycoKeys 32: 1-24. https://doi.org/10.3897/mycokeys.32.23754
Figure 6 Cylindrocladiella solicola (ex-type CMW 47198). A–C Penicillate conidiophores D–F Broadly clavate to lanceolate to fusiform vesicles G–H Penicillate conidiogenous apparatus I–J Subverticillate conidiophores K Conidia. Scale bars: A = 20 µm (apply to B–C); D = 10 µm (apply to E–F); G = 10 µm (apply to H–K).
Figure 5 from: Pham NQ, Barnes I, Chen S, Pham TQ, Lombard L, Crous PW, Wingfield MJ (2018) New species of Cylindrocladiella from plantation soils in South-East Asia. MycoKeys 32: 1-24. https://doi.org/10.3897/mycokeys.32.23754
Figure 5 Cylindrocladiella parvispora (ex-type CMW 47197). A–C Penicillate conidiophores D–F Fusoid to cylindrical vesicles G–H Penicillate conidiogenous apparatus I–J Subverticillate conidiophores K Conidia. Scale bars: A = 20 µm (apply to B–C); D = 10 µm (apply to E–F); G = 10 µm (apply to H–K).
Figure 3 from: Pham NQ, Barnes I, Chen S, Pham TQ, Lombard L, Crous PW, Wingfield MJ (2018) New species of Cylindrocladiella from plantation soils in South-East Asia. MycoKeys 32: 1-24. https://doi.org/10.3897/mycokeys.32.23754
Figure 3 Cylindrocladiella malesiana (ex-type CMW 48278). A–C Penicillate conidiophores D–F Fusoid to lanceolate vesicles G–H Penicillate conidiogenous apparatus I–J Subverticillate conidiophores K Conidia. Scale bars: A = 20 µm (apply to B–C); D = 10 µm (apply to E–F); G = 10 µm (apply to H–K).
Figure 2 from: Pham NQ, Barnes I, Chen S, Pham TQ, Lombard L, Crous PW, Wingfield MJ (2018) New species of Cylindrocladiella from plantation soils in South-East Asia. MycoKeys 32: 1-24. https://doi.org/10.3897/mycokeys.32.23754
Figure 2 Cylindrocladiella arbusta (ex-type CMW 47295). A–C Penicillate conidiophores D–F Obpyriform to lanceolate vesicles G–H Penicillate conidiogenous apparatus I–J Subverticillate conidiophores K Conidia. Scale bars: A = 20 µm (apply to B–C); D = 10 µm (apply to E–F); G = 10 µm (apply to H–K).
Figure 4 from: Pham NQ, Barnes I, Chen S, Pham TQ, Lombard L, Crous PW, Wingfield MJ (2018) New species of Cylindrocladiella from plantation soils in South-East Asia. MycoKeys 32: 1-24. https://doi.org/10.3897/mycokeys.32.23754
Figure 4 Cylindrocladiella obpyriformis (ex-type CMW 47194). A–C Penicillate conidiophores D–F Obpyriform vesicles G–H Penicillate conidiogenous apparatus I–J Subverticillate conidiophores K Conidia. Scale bars: A = 20 µm (apply to B–C); D = 10 µm (apply to E–F); G = 10 µm (apply to H–K).
Figure 1 from: Pham NQ, Barnes I, Chen S, Pham TQ, Lombard L, Crous PW, Wingfield MJ (2018) New species of Cylindrocladiella from plantation soils in South-East Asia. MycoKeys 32: 1-24. https://doi.org/10.3897/mycokeys.32.23754
Figure 1 Phylogenetic tree based on maximum likelihood (ML) analysis of a combined data set of his3, tef1, tub2 and ITS sequence alignments. Bootstrap value ≥ 60 % for maximum parsimony (MP) and ML analyses are indicated at the nodes. Bootstrap values lower than 60 % are marked with "*" and absent are marked with "–". Isolates representing ex–type material are marked with "T" and isolates collected in this study are highlighted in bold. Calonectria brachiatica (CMW 25307) and Calonectria pauciramosa (CMW 5683) represent the outgroups.
Figure 2 in Diversity of sarcosaprophagous Diptera (Calliphoridae, Sarcophagidae) in organic and conventional mango plantations in the Brazilian semi-arid region
Figure 2 Diptera species dominance ranking by management types. (a and b) Calliphoridae; (c and d) Sarcophagidae.
Figure 1 in Diversity of sarcosaprophagous Diptera (Calliphoridae, Sarcophagidae) in organic and conventional mango plantations in the Brazilian semi-arid region
Figure 1 Rarefaction (solid lines) and extrapolation (dashed lines) curves for species richness (a), diversity of common (b) and dominant species (c) of Sarcosaprophagous in both, conventional (circle) organic (triangle) managements. Shadows refer to confidence interval after 999 simulations; d) non-metric multidimensional scaling (NMDS) showing species composition distribution in both conventional (circle) organic (triangle) managements.
Figure 5 in Comparison of dung beetle communities (Coleoptera: Scarabaeidae: Scarabaeinae) in oil palm plantations and native forest in the eastern Amazon, Brazil
Figure 5 Number of dung beetle species collected in forest at different distances from the forest-oil palm plantation border.
Ecosystem resilience and pest resistance in Eucalyptus plantations is driven by understorey complexity due to forest management
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Supplementary material 2 from: Pham NQ, Marincowitz S, Chen SF, Rodas CA, Wingfield MJ (2022) Soil-borne Calonectria (Hypocreales, Nectriaceae) associated with Eucalyptus plantations in Colombia. MycoKeys 94: 17-35. https://doi.org/10.3897/mycokeys.94.96301
Collection details and GenBank accessions of isolates included in the phylogenetic analyses
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Allen Brain Atlas
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Annotated Behaviour and Observability Dataset (ABODe)
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DANDI Archive for NWB datasets
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International Brain Laboratory public data
The International Brain Laboratory public data releases expose standardized mouse decision-making experiments, including Neuropixels recordings, widefield calcium imaging, behavior, and session metadata accessed through the ONE API.
OpenNeuro
OpenNeuro is a free, open platform for sharing neuroimaging datasets, with public search, dataset pages, and download paths for web, S3, DataLad, and the OpenNeuro CLI.