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Data from: Empirical verification of feeding selectivity of larval and juvenile pelagic fishes using in situ zooplankton communities
<p>Most studies on the feeding ecology of larvae and juveniles of commercially important pelagic fishes have used field-based approaches. However, due to possible biases related to net sampling, it is uncertain whether the results obtained from those studies truly represent the situation of live fish in the sea. Here we investigated the feeding ecology of pelagic fishes through a laboratory experiment minimizing the biases inherent in field net sampling. In the experiment, hatchery-reared juvenile chub mackerel (<em>Scomber japonicus</em>) and larval/juvenile Japanese anchovy <em>(Engraulis japonicus</em>) were fed with wild-caught zooplankton assemblages collected from around Hakatajima Island in the Seto Inland Sea, Japan. The relationships between fish size and prey number in the gut, and the selectivity on each prey organism were determined. As a result, in both species, prey number and size increased with body size, and the fish showed strong selectivity for crustaceans including copepodites and adults of copepods. Our data has also clearly indicated that both species can selectively prey on preferred foods that are rare while avoiding non-preferred foods that are abundant. These results, which substantially accord with reports from previous field studies, will not only help field scientists make a convincing interpretation of their data, but also open the possibility of further laboratory studies on detailed mechanisms of the feeding selectivity of larval/juvenile pelagic fishes.</p>
Figure 1 in Composition and spatio-temporal dynamics of aquatic bird community in humid areas of Alto Parana Atlantic Forest
Figure 1. Map of the RPPN Foz do Rio Aguapeí and location of the six studied areas in the RPPN Foz do Rio Aguapeí. Legend: (1) Lagoa São Gabriel; (2) Lagoa das Piranhas; (3) Lagoa dos Porcos; (4) Constructed wetland; (5) Aguapei river –; and (6) Lagoa da sede. Sources: CESP (2013) and Google Earth (2021).
Figure 2 in Composition and spatio-temporal dynamics of aquatic bird community in humid areas of Alto Parana Atlantic Forest
Figure 2. Cumulative curve of the 52 waterfowl bird species in the RPPN Foz do Rio Aguapeí showing stability from sample 27 to 31.
Figure 3 in Composition and spatio-temporal dynamics of aquatic bird community in humid areas of Alto Parana Atlantic Forest
Figure 3. NMDS (stress of 0.097) of the spatial distribution of the aquatic bird community recorded by the transect method in the lagoons of the RPPN Foz do Aguapeí, during the dry (rounded symbols) and rainy seasons (square symbols). Legend: LS = Lagoa da Sede; LSG = Lagoa São Gabriel; LP = Lagoa da Piranha and LPO = Lagoa dos Porcos.
Fig. 6 in Toxocara canis-induced changes in host intestinal microbial communities
Fig. 6 Correlation networks of the microbiome. a Heatmap of correlation coefficients in the CI, II and Tc groups. b Network map between species. Each node in the graph represents a species, with the color of the dot representing the highest relative abundance observed within these subgroups.The size of the dot corresponds to the average relative abundance of the species, with larger dots indicating higher abundance.The species are connected to each other through straight lines, with the color pink indicating a positive correlation and blue indicating a negative correlation. The thickness of the lines reflects the magnitude of the correlation, with only correlation coefficients> 0.2 between species being displayed
Fig. 3 in Toxocara canis-induced changes in host intestinal microbial communities
Fig. 3 Comparison of beta diversity indicator of flora among CI, II and Tc groups. a Unweighted uniFrac analysis, b Weighted uniFrac analysis, c Partial least-squares discriminant analysis. CI, Intestine samples of dogs in control group; II, intestine samples of dogs in infected group; plsda, partial least-squares discriminant analysis; Tc, Toxocara canis samples
Fig. 5 in Toxocara canis-induced changes in host intestinal microbial communities
Fig. 5 Differences in species composition of flora in the CI, II and Tc group at the genus level. The horizontal coordinate is the sample name and the vertical coordinate is the relative abundance of the species annotated. Species not annotated at this taxonomic level and whose abundance was <0.5% of the sample were combined as "Others" (a). b The top 10 species at the genus level in the CI, II and TI group. Note that the significance of the test of difference was marked with an asterisk at the top of the bar graph if available. CI, Intestine samples of dogs in control group; II, intestine samples of dogs in infected group; Tc, Toxocara canis samples
Fig. 2 in Toxocara canis-induced changes in host intestinal microbial communities
Fig. 2 Boxplots showing comparisons of the alpha diversity indicators of flora among the three experimental groups. a Coverage index, b Chao index, c Shannon index, d Ace index. CI, Intestine samples of dogs in control group; II, intestine samples of dogs in infected group; Tc, Toxocara canis samples
Fig. 1 in Toxocara canis-induced changes in host intestinal microbial communities
Fig. 1 OTU cluster analysis. OTUs were generated according to 97% sequence similarity clustering. a Venn diagram of the unique and common OTUs among the three groups. b Rank-abundance curves. c Rarefaction curve. d Species accumulation curve. CI, Intestine samples of dogs in control group; II, intestine samples of dogs in infected group; OTU, operational taxonomic unit; Tc, Toxocara canis samples
Fig. 3 in Implementing a community vector collection strategy using xenomonitoring for the endgame of lymphatic filariasis elimination
Fig. 3 Cost distribution based on tspe of cost for studies in northern and southern communities, Ghana. a The recurrent costs for studies in the northern and southern communities, Ghana. b The capital costs for studies in the northern and southern communities, Ghana. Abbreviation: IEC, information, education and communication for communits engagement
Fig. 2 in Implementing a community vector collection strategy using xenomonitoring for the endgame of lymphatic filariasis elimination
Fig. 2 Validation of mosquitoes sampled bs CVCs and the research team in the northern and southern communities, Ghana. a Validation of mosquitoes sampled bs CVCs and the research team in the drs season. b Validation of mosquitoes sampled bs CVCs and the research team in the rains season. Abbreviations: VAL validation, HLC human landing collections, PSC psrethrum spras collections, WET window exit trap
Fig 2 in Monitoring and assessing the physico-chemical water properties and planktonic communities in tilapia nursing pond
Fig 2: Percentages of different phytoplankton communities during the study period (a, b c, are indicating the size category as small, medium and large)
Fig 1 in Monitoring and assessing the physico-chemical water properties and planktonic communities in tilapia nursing pond
Fig 1: Percentages of total phytoplankton and total zooplankton in all size categorized pond during the sampling period
Fig. 10 in A rare window into a back-reef fish community from the middle Miocene (late Badenian) Medobory Hills barrier reef in western Ukraine, reconstructed mostly by means of otoliths
Fig. 10 Fish teeth from the studied localities: a–e Pshekharus yesinorum Bannikov & Kotlyar, 2015, isolated jaw teeth in lateral (a1, b1, c, d1, e) and dorsal view (a2, b2, d2), arranged in a sequence from distal to proximal positions. f Dasyatis sp., anterior tooth in dorsal (f1), occlusal view (f2), profile (f3) and labial view (f4)
Fig. 7 in A rare window into a back-reef fish community from the middle Miocene (late Badenian) Medobory Hills barrier reef in western Ukraine, reconstructed mostly by means of otoliths
Fig. 7 Otoliths of Gobionellidae: a–e Deltentosteus aff. telleri (Schubert, 1906), 7a Shydlivshchyna, NMNHU-P PI 2553, b (reversed), d Kozatskyi Yar, NMNHU-P PI 2552, c (reversed), e Mlyntsi, NMB P1209. f, g Economidichthys triangularis (Weiler, 1943), f (reversed) Shydlivshchyna, NMB P1210, g (reversed) Mlyntsi, NMNHU-P PI 2554. h, i Knipowitschia polonica Schwarzhans et al., 2020a, 2020b, h Shydlivshchyna, NMNHU-P PI 2562, i Kozatskyi Yar, NMB P1213. j, k Pomatoschistus elegans (Procházka, 1900), j (reversed) Kozatskyi Yar, NMNHU-P PI 2576, k (reversed) Shydlivshchyna, NMB P1222
Fig. 4 in A rare window into a back-reef fish community from the middle Miocene (late Badenian) Medobory Hills barrier reef in western Ukraine, reconstructed mostly by means of otoliths
Fig. 4 Otoliths of Gobius spp.: a–e Gobius bratishkoi n. sp., a holotype, NMNHU-P PI 2555, Kozatskyi Yar, b–e paratypes, b (reversed) Mlyntsi, NMNHU-P PI 2556, c–e (reversed) Kozatskyi Yar, NMB P1211. f Gobius reichenbacherae Schwarzhans, 2014, Shydlivshchyna, NMNHU-P PI 2557 (reversed). g–k Gobius ukrainicus n. sp., j holotype, Shydlivshchyna, NMNHU-P PI 2558, g–i, k paratypes, g, i, k NMNHU-P PI 2560, h (reversed) Mlyntsi, NMNHU-P PI 2559
Fig. 1 in A rare window into a back-reef fish community from the middle Miocene (late Badenian) Medobory Hills barrier reef in western Ukraine, reconstructed mostly by means of otoliths
Fig. 1 Location map and stratigraphy: a schematic map showing the Medobory Reef (after Korolyuk, 1952, and Górka et al., 2012, with modifications) and the studied localities in the vicinities of Horodok, western Ukraine; b schematic geologic cross section of the Badenian sequence through the Medobory region after Wysocka et. al. (2016) and Górka (2018a)
Fig. 13 in A rare window into a back-reef fish community from the middle Miocene (late Badenian) Medobory Hills barrier reef in western Ukraine, reconstructed mostly by means of otoliths
Fig. 13 Late Badenian paleogeography of the Paratethys and distribution of selected non-gobioid otolith-based taxa through the basin. Most common species are shown in bold printing. Asterisk denotes multiple locations, of which Borský Mikuláš represents the richest and most recently described otolith assemblage (Brzobohatý et al., 2022). Double asterisk for Dentex aff. gregarius tentatively includes records of Dentex aff. maroccanus by Brzobohatý et. al. (2022). Triple asterisk for Argyrosomus sp. denotes record of Argyrosomus aff. regius by Brzobohatý et. al. (2022). Paleogeography based on Rögl (1999), Popov et. al. (2004), and KováČ et. al. (2017)
Fig. 9 in A rare window into a back-reef fish community from the middle Miocene (late Badenian) Medobory Hills barrier reef in western Ukraine, reconstructed mostly by means of otoliths
Fig. 9 Otoliths of Haemulidae, Serranidae, Sparidae, Leiognathidae and Caproidae: a (reversed)—Brachydeuterus speronatus (Bassoli, 1906), Kozatskyi Yar, NMNHU-P PI 2549. b, c Serranidae indet., b (broken and repaired), c (reversed), Kozatskyi Yar, NMNHU-P PI 2579. d, e Pshekharus yesinorum Bannikov & Kotlyar, 2015, Mlyntsi, NMNHU-P PI 2578. f (reversed)—Leiognathidae indet., Shydlivshchyna, NMB P1214. g Perciformes indet., Shydlivshchyna, NMB P1221. h (reversed) – Capros aper (Linnaeus, 1758), Mlyntsi, NMB P1206
Fig. 12 in A rare window into a back-reef fish community from the middle Miocene (late Badenian) Medobory Hills barrier reef in western Ukraine, reconstructed mostly by means of otoliths
Fig. 12 Late Badenian paleogeography of the Paratethys and distribution of gobioid otolith-based taxa through the basin. Most common species are shown in bold printing (Gobius reichenbacherae tentatively includes records of Gobius aff. niger by Brzobohatý et al., 2022). Asterisk denotes multiple locations, of which Borský Mikuláš represents the richest and most recently described otolith assemblage (Brzobohatý et al., 2022). Double asterisk denotes species only known in the Vienna Basin from the early Badenian and shown for correlation purposes. Paleogeography based on Rögl (1999), Popov et. al. (2004), and KováČ et. al. (2017)
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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.