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549 results for “habitat‐use”
Fig. 1 in Use Of Intertidal Mangrove And Sea Wall Habitats By Coral Reef Fishes In The Wakatobi Marine Park, Indonesia
Fig. 1. Map of study sites. The arrow points to Hoga Island off the northeast coast of Kaledupa Island. The entire Tukangbesi Archipelago lies within the Wakatobi National Marine Park.
Fig. 3 in Use of baits for the evaluation of underground termites (Blattodea: Rhinotermitidae) in different habitats of the southern Amazon region
Fig. 3. Queen of Heterotermes tenuis (center circle) in early stage of egg production (circle on lef), and colony formation inside the cardboard bait in southern Amazonia.
Fig. 2 in Use of baits for the evaluation of underground termites (Blattodea: Rhinotermitidae) in different habitats of the southern Amazon region
Fig. 2. Predominant termites in this study in southern Amazonia: (A) Nasutitermes sp. soldier; (B) Heterotermes tenuis soldier.
Fig. 1 in Use of baits for the evaluation of underground termites (Blattodea: Rhinotermitidae) in different habitats of the southern Amazon region
Fig. 1. Spatial arrangement of Termitrap® baits within plots for subterranean termite survey in different environments in southern Amazonia.
Fig. 2 in Use of functional traits to assess changes in stream fish assemblages across a habitat gradient
Fig. 2. Average position of species occurrence along the gradient of habitat structure (dark circles). The horizontal bars indicate the standard deviation of the mean position of each species, and the vertical bars at the bottom of the graph represent the position of each stream along the habitat gradient (axis 1 of RLQ). Species codes are presented in Table 2.
Fig. 1 in Use of functional traits to assess changes in stream fish assemblages across a habitat gradient
Fig. 1. Location of the study area in the northwestern region of São Paulo State, Brazil (black area on the country map), showing the 91 streams sampled.
Fig. 3 in Use of functional traits to assess changes in stream fish assemblages across a habitat gradient
Fig. 3. Pearson correlation between the stream scores of the first RLQ axis and the original values of the environmental variables. All correlations were significant (Pearson correlation, P <0.05), except for the proportion of bedrock in the substrate (triangle).
Fig. 4 in Use of functional traits to assess changes in stream fish assemblages across a habitat gradient
Fig. 4. Functional traits significantly correlated with the first RLQ axis (Pearson correlation, P <0.005). In each graph, the first RLQ axis represents streams with banks covered by grasses and sandy bottom (less complex) and streams with banks covered by trees/shrubs and bottom with rocks/woody debris (more complex).
FIGURE 3 in Habitat modification driven by land use as an environmental filter on the morphological traits of neotropical stream fish fauna
FIGURE 3 | Representation of significant associations (p <0.05) identified by the fourth-corner method in the factorial map of the RLQ analysis. Red denotes a positive relationship between morphological traits and environmental variables, blue indicates a negative relationship, and grey represents nonsignificant relationships. Codes: Cond: Conductivity, Rock: Rocky substrate, Woody: Woody debris, Turb: Turbidity, Backw: Backwater, DO: Dissolved Oxygen, Temp: Temperature. See acronyms for the morphological traits in Tab. S3.
FIGURE 1 in Habitat modification driven by land use as an environmental filter on the morphological traits of neotropical stream fish fauna
FIGURE 1 | Study area. Location of sampling sites according with land use covers: S1 -Manoel Gomes, S2 - Pedregulho, S3 - Arquimedes, S4 - Bom Retiro, S5 - Rio da Paz, S6 - Nene, S7 - Cascavel, S8 - Afluente do Quati, and S9 - Quati.
FIGURE 2 in Habitat modification driven by land use as an environmental filter on the morphological traits of neotropical stream fish fauna
FIGURE 2 | Relationship between morphological traits and environmental variables of the first two axes of the RLQ of the species along the lower Iguaçu River. The figures of the fish were added to illustrate the species. Codes: Woody: Woddy debris, Cond: Conductivity, Rocky: Rocky substrate, Turb: Turbidity, Backw: Backwater, DO: Dissolved Oxygen, Temp: Temperature, Anc: Ancystrus sp., Syn: Synbranchus sp., Hyp: Hypostomus sp., Hep: Heptapterus sp., Cam: Cambeva sp., Cor: Corydoras sp., Rha: Rhamdia sp., Geo: Geophagus sp., Ast: Astyanax sp., Psa: Psalidodon sp., Bry: Bryconamericus sp., Gym: Gymnotus sp., Hop: Hoplias sp., Pha: Phalloceros sp., Poe: Poecilia sp.
FIGURE 4 in Fish functional responses to local habitat variation in streams within multiple land uses areas in the Amazon
FIGURE 4 | Relationships between the ecomorphological traits of fish species and environmental variables (land use and local habitat) in the streams evaluated in this study. Traits are represented by labels: relative head length (RHL), relative mouth width (RMW), relative height (RH), relative area of pectoral fin (RAPF) and relative caudal peduncle length (RCPL).
FIGURE 3 in Fish functional responses to local habitat variation in streams within multiple land uses areas in the Amazon
FIGURE 3 | Relationships between fish functional trophic groups and environmental variables (land use and local habitat) in the streams evaluated in this study. The groups are represented by the labels: Diurnal channel drift feeders (FTG 3), Diurnal backwater drift feeders (FTG 4), Diurnal surface pickers (FTG 7), Diggers (FTG 9) and Ambush and stalking predators (FTG 11). The FTG's with a correlation between 0.2 and -0.2 have been omitted for better visualization of the results.
FIGURE 2 in Fish functional responses to local habitat variation in streams within multiple land uses areas in the Amazon
FIGURE 2 | Ordination of the types of land use in the catchment areas of the study streams at the Capim River basin, eastern Amazon.
FIGURE 1 in Fish functional responses to local habitat variation in streams within multiple land uses areas in the Amazon
FIGURE 1 | Location of sampling streams (Middle Capim River basin, Pará State, Brazil). The characteristics of each land use class are described in the Material and Methods section.
Figure 1 in Specialist and generalist species in habitat use: implications for conservation assessment in snakes
Figure 1. Relationship between the diversity scores in habitat use and the number of citations (log transformed) for each snake species in the study area. Each point is one snake species: Ca, Coronella austriaca, Cg, Coronella girondica, Hh, Hemorrhois hippocrepis, Mb, Macroprotodon brevis, Mm, Malpolon monspessulanus, Nn, Natrix natrix, Rh, Rhinechis scalaris, Vl, Vipera latastei.
Figure 2 in Specialist and generalist species in habitat use: implications for conservation assessment in snakes
Figure 2. Principal components plot for different snake species. The percentage of the variance explained by the two main factors is indicated on the axes. Three separate groups of species are indicated. Ca, Coronella austriaca, Cg, Coronella girondica, Hh, Hemorrhois hippocrepis, Mb, Macroprotodon brevis, Mm, Malpolon monspessulanus, Nn, Natrix natrix, Rs, Rhinechis scalaris, Vl, Vipera latastei.
Fig. 6 in Activity pattern and resource use of two Callosciurus species in different habitats in northeastern Thailand
Fig. 6. Proportion of food items consumed by (a) Callosciurus finlaysonii (n = 143) and (b) C. caniceps (n = 35).
Fig. 2 in Activity pattern and resource use of two Callosciurus species in different habitats in northeastern Thailand
Fig. 2. Frequencies of detection of active (a) Callosciurus finlaysonii and (b) C. caniceps in each survey time. Data are displayed as mean ± SD. Different letters in the figure indicate a significant difference (Steel-Dwass test; P <0.05).
Fig. 1 in Activity pattern and resource use of two Callosciurus species in different habitats in northeastern Thailand
Fig. 1. Location of the study site in the headquarters (HQ) of the Sakaerat Environmental Research Station and census routes. Upper figure shows the location of Sakaerat Biosphere Reserve and the bottom figure shows an enlarged view of the HQ. Solid lines show the census route of the present study, broken lines show paved survey route of the previous study (Kobayashi et al., 2019b), broken line shows non-paved survey route of the previous study (Kobayashi et al., 2019b) in natural forests (DDF: dry dipterocarp forest in light grey; DEF: dry evergreen forest in dark grey). Dotted areas in the bottom figure are relatively open spaces with few trees, white square is the nursery, and striped squares are buildings.
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
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.