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2,293 results for “Atlantic forests”
Fig. 2 in Small mammals in high fragmented landscape in Cerrado/ Atlantic Forest ecotone, Southeastern Brazil
Fig. 2. Species accumulation curves to 24 fragments together for small mammals located in southeastern Brazil.
Figs 2, 3 in Susceptibility of targets to the vampire bat Desmodus rotundus are proportional to their abundance in Atlantic Forest fragments?
Figs 2, 3. Two records of the approach of Desmodus rotundus (É. Geoffroy, 1810): 2, a bat landing on a trunk near a deer (Mazama americana); 3, a bat on the ground very close to a tapir (Tapirus terrestris).
Fig. 1 in Susceptibility of targets to the vampire bat Desmodus rotundus are proportional to their abundance in Atlantic Forest fragments?
Fig. 1. Study area located in the municipalities of ItajÁ and Aporé, state of GoiÁs, BraZil. Black dots represent the sites where the camera traps were set up.
Fig. 5 in Seasonality of dung beetles (Coleoptera: Scarabaeinae) in Atlantic Forest sites with different levels of disturbance in southern Brazil
Fig. 5. Non-metric multidimensional scaling (BraY-Curtis coefficient) for samplings of the four Atlantic Forest sites sampled in Rio Grande do Sul state, Brazil, between MaY 2016 and JulY 2017. Red circles represent the most similar clusters.
Fig. 4 in Seasonality of dung beetles (Coleoptera: Scarabaeinae) in Atlantic Forest sites with different levels of disturbance in southern Brazil
Fig. 4. Cluster analYsis of the dung beetle similaritY (Jaccard coefficient) between the four Atlantic Forest sites sampled in Rio Grande do Sul state, Brazil: Turvo State Park (TSPK); Moreno Fortes Biological Reserve (MRBR); Morro do Cerrito (MOCE); Val Feltrina (VAFE) between MaY 2016 and JulY 2017.
Fig. 3 in Seasonality of dung beetles (Coleoptera: Scarabaeinae) in Atlantic Forest sites with different levels of disturbance in southern Brazil
Fig. 3. Linear regression between the climatic variables (precipitation and temperature) and dung beetle abundance and richness sampled in Atlantic Forest sites of Rio Grande do Sul state (Turvo State Park, Moreno Fortes Biological Reserve, Morro do Cerrito, Val Feltrina) between MaY 2016 and JulY 2017.
Fig. 2 in Seasonality of dung beetles (Coleoptera: Scarabaeinae) in Atlantic Forest sites with different levels of disturbance in southern Brazil
Fig. 2. Rarefaction and extrapolation curves of the assemblages of Scarabaeinae sampled in four Atlantic Forest sites in Rio Grande do Sul state, Brazil, during MaY 2016 to JulY 2017.
Fig. 1 in Seasonality of dung beetles (Coleoptera: Scarabaeinae) in Atlantic Forest sites with different levels of disturbance in southern Brazil
Fig. 1. Location of the four Atlantic Forest sites sampled in Rio Grande do Sul state, Brazil, map and satellite images: A, Turvo State Park, Derrubadas; B, Moreno Fortes Biological Reserve, Dois IrmÃos das Missões; C, Morro do Cerrito, Santa Maria; D, Val Feltrina, Silveira Martins. Source: ArcGIS software map; satellite images Google Earth Explorer.
Fig. 6 in Do changes in riparian zones affect periphyton growth and invertebrate colonization on rocky substrates in Atlantic Forest streams?
Fig. 6. Canonical analysis of principal coordinates (CAP) of invertebrates associated with cobbles in Luxemburgo (gray circles), Macuco (black squares) and Pau Amarelo (white diamonds) streams, state of Espírito Santo, Brazil. Only taxa vectors with correlations>0.3 are included in the plot. T7, T15, T30, T45 and T60: sampling intervals (Bae: Baetidae; Calo, Calopterygidae; Chi, Chironominae; Elm.A, Elmidae adult; Elm.L, Elamidae larva; Emp, Empididae; Ger, Gerridae; Gom, Gomphidae; Hel, Helichopsychidae; Hydra, Hydracarina; Hyd.psy, Hydropsychidae; Hyd.ptil, Hydroptilidae; Lep.cer, Leptoceridae; Lep.hyp, Leptohyphidae; Lep.phl, Leptophlebiidae; Meg, Megapodagrionidae; Nau, Naucoridae; Odo, Odontoceridae; Oli, Oligochaeta; Ort, Orthocladiinae; Per, Perlidae; Philo, Philopotamidae; Poly, Polycentropodidae; Pse, Psephenidae; Psy, Psychodidae; Tany, Tanypodinae; Vel, Veliidae).
Fig. 3 in Do changes in riparian zones affect periphyton growth and invertebrate colonization on rocky substrates in Atlantic Forest streams?
Fig. 3. Values (mean ± SE) of invertebrate density associated with cobbles in Luxemburgo (thin solid line, gray circles), Macuco (thick solid line, black squares) and Pau Amarelo (dashed line, white diamonds) streams, state of Espírito Santo, Brazil.
Fig. 5 in Do changes in riparian zones affect periphyton growth and invertebrate colonization on rocky substrates in Atlantic Forest streams?
Fig. 5. Species accumulation curves (Mao-Tau sampled based rarefaction with 95% confidence intervals) of invertebrates associated with cobbles in Luxemburgo (thin solid line, gray circles), Macuco (thick solid line, black squares) and Pau Amarelo (dashed line, white diamonds) streams, state of Espírito Santo, Brazil.
Fig. 1 in Do changes in riparian zones affect periphyton growth and invertebrate colonization on rocky substrates in Atlantic Forest streams?
Fig. 1. Daily mean values of water temperature (lines) and luminosity (columns) in Luxemburgo (gray), Macuco (black) and Pau Amarelo (white) streams, state of Espírito Santo, Brazil during the experiment.
Fig. 2 in Do changes in riparian zones affect periphyton growth and invertebrate colonization on rocky substrates in Atlantic Forest streams?
Fig. 2. Contents of chlorophyll-a (mean ± SE) on the cobbles incubated in Luxemburgo (thin solid line, gray circles), Macuco (thick solid line, black squares) and Pau Amarelo (dashed line, white diamonds) streams, state of Espírito Santo, Brazil.
Fig. 7 in Breeding biology and conservation of hawk-eagles (Spizaetus spp.) Aves, Accipitridae) in southern Atlantic Forest, Brazil
Fig. 7. Nesting phenology of Ornate Hawk-Eagle (nest C). Chronological sequence from upper left to bottom right: nest with an egg (27 Sep 2008); egg; (27 Sep 2008); nestling – few days old (08 Nov 2008); adult on nest (16 Nov 2008); nestling about 10 days old (19 Nov 2008); nestling about 20 days old (28 Nov 2008); nestling about 40 days old (Dec 2008); Fledging (Apr 2009); Nest without chamber or traces of use (Apr 2009).
Fig. 6 in Breeding biology and conservation of hawk-eagles (Spizaetus spp.) Aves, Accipitridae) in southern Atlantic Forest, Brazil
Fig. 6. Nest of an Ornate Hawk-Eagle located 31 m in an Araucaria tree (DBH = 132 cm). Lateral view (upper right) and view from above (bottom right) with details of the chamber (with green leaves and sticks).
Fig. 4 in Breeding biology and conservation of hawk-eagles (Spizaetus spp.) Aves, Accipitridae) in southern Atlantic Forest, Brazil
Fig. 4. Nest of an Ornate Hawk-Eagle built 20 m in a Myrtaceae tree (DBH = 78.94 cm) (red circle). Lateral view (upper right) and view from above (bottom right) of the nest.
Fig. 2 in Breeding biology and conservation of hawk-eagles (Spizaetus spp.) Aves, Accipitridae) in southern Atlantic Forest, Brazil
Fig. 2. Extent of occurrence of the Ornate Hawk-Eagle in the southern Atlantic Forest, Brazil based on historical (before 2000s; red triangles and red dashed line) and current records (after 2000s; black dots and line). Atlantic Forest remnants are showed in light green.
Fig. 1 in Breeding biology and conservation of hawk-eagles (Spizaetus spp.) Aves, Accipitridae) in southern Atlantic Forest, Brazil
Fig. 1. Extent of occurrence of the Black-and-white Hawk-Eagle in the southern Atlantic Forest, Brazil based on historical (before 2000s; red triangles and red dashed line) and current records (after 2000s; black dots and line). Atlantic Forest remnants are showed in light green.
Fig. 3 in Breeding biology and conservation of hawk-eagles (Spizaetus spp.) Aves, Accipitridae) in southern Atlantic Forest, Brazil
Fig. 3. Extent of occurrence of the Black Hawk-Eagle in the southern Atlantic Forest, Brazil based on historical (before 2000s; red triangles and red dashed line) and current records (after 2000s; black dots and line). Atlantic Forest remnants are showed in light green.
Fig. 2 in Helminths of sigmodontine rodents in an agroforestry mosaic in the Brazilian Atlantic Forest: Patterns and processes of the metacommunity structure
Fig. 2. Ordinated matrices for the helminths metacommunity at Pratigi Environmental Protection Area, municipality of Igrapiúna, state of Bahia, northeast Brazil. A) Infracommunities and B) Component Communities.
ScienceDex guides
Understand access before you commit
These curated guides explain access requirements, typical timelines, costs, and reuse considerations for widely used research datasets.
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.