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Figure 1 in Multi-scale patterns in the host specificity of plant-dwelling arthropods: the influence of host plant and temporal variation on species richness and assemblage composition of true bugs (Hemiptera)
Figure 1. Interactions between plant species sampled and sampling period for (A) abundance (number of individuals) per plant and (B) species richness per plant (standard error bars are shown).
Figure 6 in Multi-scale patterns in the host specificity of plant-dwelling arthropods: the influence of host plant and temporal variation on species richness and assemblage composition of true bugs (Hemiptera)
Figure 6. Relationship between the effectively specialized fauna (squares) and singleton species (circles) for the number of hemipteran species from each sampling period and for the entire collection. An exponential decay equation is fitted for effectively specialized fauna, y = 2.973∗ exp (−0.00575∗ x) + (−1.478), R2 = 0.7598, and for singleton species, y = 22.53∗exp (−0.08466∗x) + 0.2614, R2 = 0.9873.
Figure 3 in Aquatic macroinvertebrate assemblages associated with root masses of water hyacinths, Eichhornia crassipes (Mart.) Solms-Laubach, 1883 (Commelinales: Pontederiaceae) in Taabo Lake, Ivory Coast
Figure 3. Hierarchical clustering, based on similarities in aquatic macroinvertebrate assemblages, of the sampling stations with a Ward linkage method and a Euclidian distance; Sa, Sahoua; Ah, Ahondo; Tc, Taabo cité; Co, Courandjourou; Tv, Taabo village.
Figure 5 in Aquatic macroinvertebrate assemblages associated with root masses of water hyacinths, Eichhornia crassipes (Mart.) Solms-Laubach, 1883 (Commelinales: Pontederiaceae) in Taabo Lake, Ivory Coast
Figure 5. Canonical correspondence analysis (CCA) diagram of macroinvertebrates collected from water hyacinth samples in relation to nine independent environmental variables measured: Temp., temperature; NH +, ammonium; pH; Trans., transparency; NO –, nitrate; Turb., 4 3 turbidity; PO 3–, phosphate; O, dissolved oxygen; and CND, conductivity.
Figure 2 in Aquatic macroinvertebrate assemblages associated with root masses of water hyacinths, Eichhornia crassipes (Mart.) Solms-Laubach, 1883 (Commelinales: Pontederiaceae) in Taabo Lake, Ivory Coast
Figure 2. Box-plots showing differences in physical and chemical variables between the two seasons (Rs = rainy season and Ds = dry season); box corresponds to 50% of the values, the square in the box corresponds to the median value and the vertical bars correspond to the minimum/maximum values.
Figure 1 in Aquatic macroinvertebrate assemblages associated with root masses of water hyacinths, Eichhornia crassipes (Mart.) Solms-Laubach, 1883 (Commelinales: Pontederiaceae) in Taabo Lake, Ivory Coast
Figure 1. Map of the man-made Taabo Lake, showing sampling stations (UTM, Universal Transverse Mercator) (Kouassi 2007).
Figure 4 in Aquatic macroinvertebrate assemblages associated with root masses of water hyacinths, Eichhornia crassipes (Mart.) Solms-Laubach, 1883 (Commelinales: Pontederiaceae) in Taabo Lake, Ivory Coast
Figure 4. Box-plots showing differences in physical and chemical variables between the three clusters (I, II and III) identified on Figure 3; box corresponds to 50% of the values, the square in the box corresponds to the median value and the vertical bars correspond to the minimum/ maximum values; n = 10. (Continued)
Figure 1 in Anuran assemblage in a rice field agroecosystem in the Pantanal of central Brazil
Figure 1. Average temperatures (dotted line), cumulative monthly rainfall (solid line), species richness (light bars) and abundance of anurans (black bars) recorded in rice fields of Fazenda San Francisco, Miranda, MS, Brazil, from May 2007 to March 2008. The asterisk (*) indicates the months when the fields were flooded.
Figure 2 in Anuran assemblage in a rice field agroecosystem in the Pantanal of central Brazil
Figure 2. Absolute abundance of eight anuran species found in the rice fields of Fazenda San Francisco, Miranda, MS, Brazil, from May 2007 to March 2008.
Figure 6 in An austral anuran assemblage in the Neotropics: seasonal occurrence correlated with photoperiod
Figure 6. Similarity of calling season for males of 18 anuran species recorded between August 2005 and July 2006. The rectangles indicate groups with overlap greater than 70%. r5cophenetic correlation coefficient. Group I: species that called mainly during spring and summer; group II: species that called only during summer; group III: species that called during spring; group IV: species that called throughout the year, except in summer. Species abbreviations follow Figure 3.
Figure 5 in An austral anuran assemblage in the Neotropics: seasonal occurrence correlated with photoperiod
Figure 5. Scatter diagrams representing the correlation of the photoperiod with richness (A) and with abundance (B) of anurans in calling activities (rs50.70 and P50.01; rs50.73 and P,0.01, respectively) between August 2005 and July 2006.
Figure 4 in An austral anuran assemblage in the Neotropics: seasonal occurrence correlated with photoperiod
Figure 4. Rose diagram of circular analysis of richness (A) and abundance (B) of calling males of 18 anuran species in calling activity between August 2005 and July 2006 in the municipality of Itaara, southern Brazil. The angles represent the months. The length of the mean vector (r) is a measure of concentration of data around the year.
Figure 3 in An austral anuran assemblage in the Neotropics: seasonal occurrence correlated with photoperiod
Figure 3. Similarity of habitat use for males of 18 anuran species recorded in three sites in the municipality of Itaara, southern Brazil. The rectangles indicate groups with overlap up to 90%. r5cophenetic correlation coefficient. Group I: species in permanent ponds; group II: species in permanent ponds and neighbouring swampy regions; group III: species in permanent ponds and dam backwater; group IV: species in permanent ponds, open dam and dam backwater; group V: species in permanent and temporary ponds; group VI: species in permanent and temporary ponds and dam backwater. Species: Aplastodiscus perviridis (Ape), Chaunus achavali (Cac), Dendropsophus minutus (Dmi), D. sanborni (Dsa), Elachistocleis bicolor (Ebi), Hypsiboas faber (Hfa), Hypsiboas pulchellus (Hpu), Leptodactylus fuscus (Lfu), L. gracilis (Lgr), L. ocellatus (Loc), Limnomedusa macroglossa (Lma), Physalaemus cf. gracilis (Pgr), P. cuvieri (Pcu), Pseudis minuta (Pmi), Pseudopaludicola falcipes (Pfa), Scinax fuscovarius (Sfu), S. granulatus (Sgr), S. squalirostris (Ssq).
Figure 1 in An austral anuran assemblage in the Neotropics: seasonal occurrence correlated with photoperiod
Figure 1. Monthly rainfall and maximum and minimum mean air temperatures throughout the period of study, August 2005–July 2006.
Figure 5 in Nematode assemblages from submarine caves in Hong Kong
Figure 5. Hierarchical clustering and MDS ordination of nematode species assemblages, using group average linkage of Bray-Curtis similarity calculated on log (x+1) transformed species abundance data (averaged across three replicates). The groups of sites separated at approximately 25% similarity threshold on the dendrogram are super-imposed on the ordination plot.
Figure 4 in Nematode assemblages from submarine caves in Hong Kong
Figure 4. The distribution of nematode feeding groups among species at the study sites. Each bar represents an average of three replicates.
Figure 2. K in Nematode assemblages from submarine caves in Hong Kong
Figure 2. K-dominance curves to compare diversity among sampling sites. Each curve represented an average value of three replicates.
Figure 1 in Nematode assemblages from submarine caves in Hong Kong
Figure 1. Lateral sections of the submarine caves surveyed, showing the layout of meiofaunal sampling stations at Steep Island Cave (SI-B) and Conic Island Cave (CI-A, CI-B, CI-C and CI-D) (after Hodgson, PP).
Figure 2 in Demersal faunal assemblages in the deep waters of the eastern Ionian Sea
Figure 2. Dendrogram of the abundance values (N/h) of the species caught in the different stations of the eastern Ionian Sea. (A5shallowest stations: 300–500 m, B15intermediate stations: 500–700 m, B25deepest stations: 700–900 m; the depths are given in m after the station numbers.)
Figure 3 in Demersal faunal assemblages in the deep waters of the eastern Ionian Sea
Figure 3. MDS plot based on the abundance (N/h) of the species in the different stations of the eastern Ionian Sea. (A5shallowest stations: 300–500 m, B15intermediate stations: 500– 700 m, B25deepest stations: 700–900 m.)
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.