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645 results for “Spatial distributions”
Figure 4 in Spatial distribution of ichthyofauna in the northern Alboran Sea (western Mediterranean)
Figure 4. Species rarefaction curves for the fish assemblages within the inner continental shelf (IS, 30–100 m), outer continental shelf (OS, 100–200 m), upper continental slope (US, 200– 500 m) and middle continental slope (MS, 500–800 m). The x-axis represents the number of samples for each group.
Figure 2 in Spatial distribution of ichthyofauna in the northern Alboran Sea (western Mediterranean)
Figure 2. Non-metric multidimensional scaling (nMDS) analyses using (a) abundance and (b) biomass of fish species collected in the different hauls.
Figure 1 in Spatial distribution of ichthyofauna in the northern Alboran Sea (western Mediterranean)
Figure 1. Map of the study area throughout the northern Alboran Sea showing the haul stations from the MEDITS survey series, from 1994 to 2005 (black points) and sampled stations from RADMED (Radiales del Mediterráneo) programme (black crosses).
Figure 3 in Spatial distribution of ichthyofauna in the northern Alboran Sea (western Mediterranean)
Figure 3. Mean values of (a) abundance (ind h−1), (b) biomass (kg h−1) and (c) species mean weight (g ind–1) in the different assemblages characterised. IS: Inner continental shelf (30–100 m); OS: outer continental shelf (100–200 m); US: upper continental slope (200–500 m); MS: middle continental slope (500–800 m). Bars represent ± standard error (SE).
Figure 7 in Spatial distribution and substrate selection by the orb-weaver spider Eustala perfida Mello-Leitão, 1947 (Araneae: Araneidae)
Figure 7. Mean density of spiders at three plots recorded altitudes of Serra do Japi (altitudes: DAE = 850 m; BASE = 1000 m; TV = 1294 m).
Figure 5 in Spatial distribution and substrate selection by the orb-weaver spider Eustala perfida Mello-Leitão, 1947 (Araneae: Araneidae)
Figure 5. (A) Female of Eustala perfida in substrate containing lichens and mosses; (B) E. perfida in the centre of the web, apart of the stem about 2 cm; (C) frequency of sites with and without concavities in tree trunks (expected) (n = 875) and frequency of spiders found in sites with and without depression (observed) (n = 100). Photographs: Y.F. Messas.
Figure 4 in Spatial distribution and substrate selection by the orb-weaver spider Eustala perfida Mello-Leitão, 1947 (Araneae: Araneidae)
Figure 4. (A) Comparison of the frequencies of diameter of available tree trunks and trunks where Eustala perfida was found; (B) number of trees, by diameter classes, in the areas of Tv Cultura, DAE and Base.
Figure 3 in Spatial distribution and substrate selection by the orb-weaver spider Eustala perfida Mello-Leitão, 1947 (Araneae: Araneidae)
Figure 3. (A) Frequency of smooth and rough trunks with diameters up to 10 cm (n = 413) in samples of plots and occurrence of Eustala perfida on them (n = 158); (B) frequency of each subcategory of tree trunks and frequency of occupation by Eustala perfida on them.
Figure 2 in Spatial distribution and substrate selection by the orb-weaver spider Eustala perfida Mello-Leitão, 1947 (Araneae: Araneidae)
Figure 2. Colour patterns of Eustala perfida and one event of predation of a female by an araneophagic spider (Gelanor sp., Mimetidae). The total body length of adult individuals is approximately 6 mm. Photographs: Y.F. Messas.
Figure 1 in Spatial distribution and substrate selection by the orb-weaver spider Eustala perfida Mello-Leitão, 1947 (Araneae: Araneidae)
Figure 1. (A) Adult female of Eustala perfida camouflaged on a trunk covered by lichen and moss. The arrow indicates spider position; (B) frontal; (C) lateral views of webs of adult female. Photographs: Y.F. Messas.
Figure 4 in Seasonal population fluctuation and spatial distribution of Orthoptera in two grassland areas of Attica - Greece
Figure 4. Mean number of Chorthippus bornhalmi per sample in the mountain station through a 2-year study.
Figure 3 in Seasonal population fluctuation and spatial distribution of Orthoptera in two grassland areas of Attica - Greece
Figure 3. Mean number of Dociostaurus maroccanus per sample in the lowland station through a 2-year study.
Figure 1 in Seasonal population fluctuation and spatial distribution of Orthoptera in two grassland areas of Attica - Greece
Figure 1. Mean number of individuals per sample of Acrididae, Tettigoniidae and Gryllidae families in the lowland station through a 2-year study.
Figure 2 in Seasonal population fluctuation and spatial distribution of Orthoptera in two grassland areas of Attica - Greece
Figure 2. Mean number of individuals per sample of Acrididae, Tettigoniidae and Gryllidae families in the mountain station through a 2-year study.
Figure 5 in Spatial distribution of Neoergasilus japonicus (Copepoda: Ergasilidae) on the fins of bluegill (Lepomis macrochirus)
Figure 5. Minimum distances of individuals between Neoergasilus japonicus on the left (A) and right (B) sides in the soft ray area of the dorsal fin of Lepomis macrochirus. Dots show the positions of copepods, and 30 and 35 minimum distances were measured.
Figure 4 in Spatial distribution of Neoergasilus japonicus (Copepoda: Ergasilidae) on the fins of bluegill (Lepomis macrochirus)
Figure 4. Available areas (= Thiessen polygons) for individuals of Neoergasilus japonicus on the left (A) and right (B) sides in the soft ray area of the dorsal fin of Lepomis macrochirus. Dots show the positions of copepods, and the available areas were measured for 23 and 25 polygons on the left and right sides, respectively.
Figure 3 in Spatial distribution of Neoergasilus japonicus (Copepoda: Ergasilidae) on the fins of bluegill (Lepomis macrochirus)
Figure 3. Proportion of occurrence of Neoergasilus japonicus on various sections of the dorsal (A) and anal (B) fins of Lepomis macrochirus at different numbers of copepods (1–10, 11–20, 21–30 and> 31 in the dorsal fin; 1–5, 6–10, 11–15 and> 16 in the anal fin). The number of L. macrochirus examined is shown in parentheses.
Figure 2 in Spatial distribution of Neoergasilus japonicus (Copepoda: Ergasilidae) on the fins of bluegill (Lepomis macrochirus)
Figure 2. Number of Neoergasilus japonicus on various sections of the dorsal (A) and anal (B) fins of Lepomis macrochirus.
Figure 4 in Motile homes: a comparison of the spatial distribution of epibiont communities on Mediterranean sea turtles
Figure 4. Diagrammatic representation of the different spatial patterns of the epibiont Chelonibia caretta found on loggerhead turtles and green turtles. (a) Total number of barnacles found for each scute; (b) mean basal area (mm2) of the barnacles for each scute; (c) percentage cover for individual scutes.
Figure 1 in Motile homes: a comparison of the spatial distribution of epibiont communities on Mediterranean sea turtles
Figure 1. Relative abundance of Chelonibia testudinaria on (a) loggerhead and (b) green turtles. Note: 47.4% and 69.7% of loggerhead and green turtles hosted no epibionts.
ScienceDex guides
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These curated guides explain access requirements, typical timelines, costs, and reuse considerations for widely used research datasets.
Allen Brain Atlas
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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.