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Fig. 1 in Who Steals the Eggs? Coprophanaeus Telamon (Erichson) Buries Decomposing Eggs in Western Amazonian Rain Forest (Coleoptera: Scarabaeidae)
Fig. 1. Superficial traces of burying activity of Coprophanaeus telamon telamon (Erichson) directly at a ''nest.'' At other places, burial traces were much less conspicuous.
Distribution. Okapis are endemic to the rain forests of the N & NE DR Congo, and the Ituri forest in particular. in Giraffidae
Distribution. Okapis are endemic to the rain forests of the N & NE DR Congo, and the Ituri forest in particular.
FIGURE 4. Fungus-harvestman interaction. A in First record of the interaction between the arthropod-pathogenic fungus Gibellula and a new species of harvestman Auranus (Stygnidae) narrowly endemic to the Brazilian rain forest
FIGURE 4. Fungus-harvestman interaction. A) Habitus of male Auranus quilombola sp. nov. without fungus infection. B) A. quilombola sp. nov. male, parasitized by arthropod-pathogenic fungus Gibellula sp. C) Details of the fungus Gibellula sp. parasitizing the harvestman A. quilombola sp. nov. (blue arrow shows the mycelium; red arrow shows the perithecium).
FIGURE 3 in First record of the interaction between the arthropod-pathogenic fungus Gibellula and a new species of harvestman Auranus (Stygnidae) narrowly endemic to the Brazilian rain forest
FIGURE 3. Distribution map of Auranus quilombola sp. nov. and other Auranus species. A) Records of A. quilombola sp. nov. in Brejos de Altitude of Ceará state. Black dots are the known records, red arrow is the location of observation of fungusharvestmen interaction, full line is the Brejos Cearenses area of endemism delimitation. B) Distribution of Auranus species in the Amazon forest according Colmenares et al. (2016) and the new species in Atlantic forest. In detail, South America with the two great blocks of rain forest, Amazonian and Atlantic forest, showing the geographic locations of A and B.
FIGURE 2 in First record of the interaction between the arthropod-pathogenic fungus Gibellula and a new species of harvestman Auranus (Stygnidae) narrowly endemic to the Brazilian rain forest
FIGURE 2. Penis of Auranus quilombola sp. nov. (Holotype, UFPB OP-901), dorsal view on the left, lateral view at the center, and ventral view on the right. Details of macrosetae are shown with colors. Scale = 0.25 mm.
Subspecies and Distribution. P. p. pardus Linnaeus, 1758 — Sudan and NE Zaire. P. p. adersi Pocock, 1932 — Zanzibar I (could be extinct). P. p. adusta Pocock, 1927 — Ethiopian highlands. P. p. ciscaucasicus Satunin, 1914 — Caucasus mountains. P. p. dathei Zukowsky, 1959 — S and C Iran (of dubious validity). P. p. delacouri Pocock, 1930 — S China to Malay Peninsula. P. p. fusca Meyer, 1794 — Indian subcontinent. P. p. japonensis Gray, 1862 — NC China. P. p. jarvisi Pocock, 1932 — Sinai Peninsula. P. p. kotiya Deraniyagala, 1949 — Sri Lanka. P. p. leopardus Schreber, 1777 — Rain forests of W and C Africa. P. p. melanotica Gunther, 1775 — S Africa. P. p. melas Cuvier, 1809 — Java. P. p. nanopardus Thomas, 1904 — Somali arid zone. P. p. nimr Hemprich & Ehrenberg, 1833 —S Israel to Arabian peninsula. P. p. orientalis Schlegel, 1857 — Russian Far East, Korea, and NE China. P. p. panthera Schreber, 1777 — N Africa. P. p. pernigra Gray, 1863 — Kashmir through Nepal to SW Xizang and Sichuan. P. p. reichenow: Cabrera, 1918 — Savannas of Cameroon. P. p. ruwenzori Camerano, 1906 — Ruwenzori and Virunga mountains of Zaire, Rwanda, and Burundi. P. p. saxicolor Pocock, 1927 — N Iran and S Turkmenistan E to Afghanistan. P. p. sindica Pocock, 1930 — SE Afghanistan through W and S Pakistan. P. p. suahelicus Neumann, 1900 — E Africa, from Kenya S to Mozambique. P. p. tulliana Valenciennes, 1856 — Turkey. in Felidae
Subspecies and Distribution. P. p. pardus Linnaeus, 1758 — Sudan and NE Zaire. P. p. adersi Pocock, 1932 — Zanzibar I (could be extinct). P. p. adusta Pocock, 1927 — Ethiopian highlands. P. p. ciscaucasicus Satunin, 1914 — Caucasus mountains. P. p. dathei Zukowsky, 1959 — S and C Iran (of dubious validity). P. p. delacouri Pocock, 1930 — S China to Malay Peninsula. P. p. fusca Meyer, 1794 — Indian subcontinent. P. p. japonensis Gray, 1862 — NC China. P. p. jarvisi Pocock, 1932 — Sinai Peninsula. P. p. kotiya Deraniyagala, 1949 — Sri Lanka. P. p. leopardus Schreber, 1777 — Rain forests of W and C Africa. P. p. melanotica Gunther, 1775 — S Africa. P. p. melas Cuvier, 1809 — Java. P. p. nanopardus Thomas, 1904 — Somali arid zone. P. p. nimr Hemprich & Ehrenberg, 1833 —S Israel to Arabian peninsula. P. p. orientalis Schlegel, 1857 — Russian Far East, Korea, and NE China. P. p. panthera Schreber, 1777 — N Africa. P. p. pernigra Gray, 1863 — Kashmir through Nepal to SW Xizang and Sichuan. P. p. reichenow: Cabrera, 1918 — Savannas of Cameroon. P. p. ruwenzori Camerano, 1906 — Ruwenzori and Virunga mountains of Zaire, Rwanda, and Burundi. P. p. saxicolor Pocock, 1927 — N Iran and S Turkmenistan E to Afghanistan. P. p. sindica Pocock, 1930 — SE Afghanistan through W and S Pakistan. P. p. suahelicus Neumann, 1900 — E Africa, from Kenya S to Mozambique. P. p. tulliana Valenciennes, 1856 — Turkey.
Wind dispersal and 1-year survival of Vataireopsis iglesiasii (Fabaceae) seedlings in a Neotropical lowland rain forest
<p>Populations of many tropical tree species are regulated by negative distance- and density-dependent processes (NDD), yet most studies on the effects of conspecific seedling and adult neighbours on seedling survival have focused on animal-dispersed species. Species with seeds dispersed by wind may not be moved as far on average as seeds dispersed by animals, but some seeds may be dispersed a lot further, suggesting that knowledge of dispersal mechanism may help in our understanding of NDD. In this study, we took advantage of a high-fecundity reproductive event that occurred for an individual isolated canopy tree of Vataireopsis iglesiasii in a tropical lowland rain forest site in Amazonian Ecuador to document seed dispersal and seedling survival to 1-year post-dispersal. Most seeds did not disperse far: 86% of germinated seedlings were found within 100 m. Mortality was high: only 49 of the 1732 monitored seedlings survived one year and only five survived a further four years. We found a significant negative effect of conspecific seedling density (but no effect of distance from the parent tree) on 1-year survival. Rare long-distance dispersal events may increase the probability of a seed reaching specific habitats, such as high-light patches, and surviving beyond one year, thereby shifting the population recruitment curve outwards away from adult trees and maintaining diversity in species-rich forests.</p>
FIGURE 3. Ceraceomyces basidiospores. A in Ceraceomyces atlanticus (Amylocorticiales, Basidiomycota), a new species from the Atlantic Rain Forest, Brazil
FIGURE 3. Ceraceomyces basidiospores. A) C. atlanticus, isotype; B) C. subapiculatus, holotype; C) C. tessulatus, Ryvarden 48532; D) C. tessulatus, F. Oldervik 032.05.
FIGURE 1 in Ceraceomyces atlanticus (Amylocorticiales, Basidiomycota), a new species from the Atlantic Rain Forest, Brazil
FIGURE 1. Phylogenetic reconstruction of Maximum Parsimony (MP), Maximum Likelihood (ML) and Bayesian analysis (BA) based on LSU rDNA sequence data showing the position of C. atlanticus with Amylocorticiales species. Bootstrap values (%) were generated from maximum parsimony (MP) and maximum likelihood (ML) analysis (10,000 bootstraps, respectively) and 1,000,000 generations to Bayesian analysis. Values above 50% in the MP and ML analyses and above 0.8 in the BA analysis are shown in the tree, which is rooted with Jaapia argillacea and J. ochroleuca.
FIGURE 2. Ceraceomyces atlanticus. A in Ceraceomyces atlanticus (Amylocorticiales, Basidiomycota), a new species from the Atlantic Rain Forest, Brazil
FIGURE 2. Ceraceomyces atlanticus. A) section through basidioma, B) vesicle from basal tissue, C) basidia, D) basidiospores. Isotype.
FIGURE 1. Miconia angustidentata. A. Habit. B in A new Miconia (Melastomataceae: Miconieae) from upland rain forest of northwestern Guyana
FIGURE 1. Miconia angustidentata. A. Habit. B. Representative larger leaves at a node (adaxial surface on left and abaxial surface on right). C. Enlargement of indumentum detail on abaxial leaf surface. D. Inflorescence showing flower buds and bracts. E. Flower (profile view) showing hypanthium, petals, stamens, and style. F. Representative petal (adaxial surface). G. Representative stamen (profile view). H. Longitudinal section of flower showing hypanthium and superior ovary with ovules. I. Representative seeds. All drawn from Clarke et al. 5181.
FIGURE 2. Manihot macrocarpa. A. Flowering branch. B. Pistillate bud with bract and bracteoles. C. Staminate bud. D. Pistillate flower. E. Fruit. F in Manihot macrocarpa (Euphorbiaceae), an unusual rain forest species from Brazil
FIGURE 2. Manihot macrocarpa. A. Flowering branch. B. Pistillate bud with bract and bracteoles. C. Staminate bud. D. Pistillate flower. E. Fruit. F. Seed, frontal and lateral view (Martins & Ledo 1928, holotype; drawn by M. Martins).
FIGURE 1. Manihot macrocarpa. A in Manihot macrocarpa (Euphorbiaceae), an unusual rain forest species from Brazil
FIGURE 1. Manihot macrocarpa. A. Habit showing several branches covering the canopy of a tree. B. Detail of stem showing diameter. C. Clasping petiole. D. Leaves. E. Staminate buds F. Inflorescence G. Fruit. (A–G by M. Martins).
FIGURE 5. Sheet 1 in Untangling the type collection and recircunscription of Pseudolaelia corcovadensis: a threatened orchid species from Brazilian Atlantic Rain Forest
FIGURE 5. Sheet 1 of the specimen Santos Lima & Brade 13325 of Pseudolaelia vellozicola, showing the label in Brade's handwriting in which he wrote "forma" below the species name.
FIGURE 6. Sheet 2 in Untangling the type collection and recircunscription of Pseudolaelia corcovadensis: a threatened orchid species from Brazilian Atlantic Rain Forest
FIGURE 6. Sheet 2 of the specimen Santos Lima & Brade 13325 of Pseudolaleia vellozicola (RB 26627). In the capsule there are flowers of a specimen of unknown precedence of P. corcovadensis.
FIGURE 7. 1 in Untangling the type collection and recircunscription of Pseudolaelia corcovadensis: a threatened orchid species from Brazilian Atlantic Rain Forest
FIGURE 7. 1. Flower of Pseudolaelia vellozicola collected in São Fidélis, municipality of Rio de Janeiro, from the specimen M.S. Wängler et al. 1613 (RB). 2. Flower of Pseudolaelia corcovadensis collected in Petrópolis, municipality of Rio de Janeiro, from the specimen M.S. Wängler et al. 1806 (RB).
FIGURE 4. Sheet 3 in Untangling the type collection and recircunscription of Pseudolaelia corcovadensis: a threatened orchid species from Brazilian Atlantic Rain Forest
FIGURE 4. Sheet 3 of the isolectotype of P. corcovadensis collected on the Morro do Corcovado by Voll & Carris s.n. (RB 26626) with a label in different handwriting from that of A. C. Brade (in Sheet 1) and a note by Antônio Toscano de Brito, which points out the erroneous indication of the specimen as an isotype.
FIGURE 3. Sheet 2 in Untangling the type collection and recircunscription of Pseudolaelia corcovadensis: a threatened orchid species from Brazilian Atlantic Rain Forest
FIGURE 3. Sheet 2 of the isolectotype of P. corcovadensis collected on the Morro do Corcovado by Voll & Carris s.n. (RB 26626): only flower dissected and stuck in the yellow capsule by Brade. The remaining materials are not part of the isolectotype and are a specimen of unknown procedence P. vellozicola: fragments within the white capsule and parts of inflorescence axes.
FIGURE 2. Sheet 1 in Untangling the type collection and recircunscription of Pseudolaelia corcovadensis: a threatened orchid species from Brazilian Atlantic Rain Forest
FIGURE 2. Sheet 1 of the lectotype of P. corcovadensis collected on the Morro do Corcovado by Voll & Carris s.n. (RB 26626) showing the label with Brade's handwriting and the collecting data.
FIGURE 1 in Untangling the type collection and recircunscription of Pseudolaelia corcovadensis: a threatened orchid species from Brazilian Atlantic Rain Forest
FIGURE 1. Distribution of Pseudolaelia corcovadensis in the state of Rio de Janeiro, municipalities of Rio de Janeiro (1), Paty do Alferes (2), Petrópolis (3), Nova Friburgo (4) Sapucaia (5); and in the state of Minas Gerais, municipality of Juíz de Fora (6).
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Allen Brain Atlas
Allen Brain Atlas is an Allen Institute collection of brain map atlases, datasets, APIs, and analysis tools covering mouse, human, and non-human primate brain resources.
Annotated Behaviour and Observability Dataset (ABODe)
ABODe is a University of Edinburgh DataShare dataset for behavior classification in group-housed mice using home-cage video, identities, bounding boxes, ground-plate positions, and annotator labels.
DANDI Archive for NWB datasets
DANDI is a BRAIN Initiative archive for publishing and sharing neurophysiology data, including electrophysiology, optophysiology, and behavioral data packaged as NWB and related standards.
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.