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Figure 5 in The southernmost occurrence of Ichthyosaurus from the Sinemurian of Portugal
Figure 5. Distribution of Ichthyosaurus sites in the Early Jurassic (the site indicated by arrow is Alberta, Canada), modified from Price et al. (2016).
Figure 1 in The southernmost occurrence of Ichthyosaurus from the Sinemurian of Portugal
Figure 1. The documented localities where ichthyosaur fossils have been uncovered, within the Lusitanian Basin (locations along the coast are Early Jurassic). Adapted from Blanco (1995).
Figure 4 in The youngest occurrence of embolomeres (Tetrapoda: Anthracosauria) from the Sunjiagou Formation (Lopingian, Permian) of North China
Figure 4. Detailed look on the ornamentation pattern of the notch and ventromedial edge of the descending flange of the pterygoid. Scale bar equals 50 mm. The zoomed-in photos on the bottom are not to scale.
Figure 5 in The youngest occurrence of embolomeres (Tetrapoda: Anthracosauria) from the Sunjiagou Formation (Lopingian, Permian) of North China
Figure 5. Phylogeny and biogeography of embolomeres. The cladogram is calibrated based on the ages of the fossils. Carboniferous localities include northern England (Anthracosaurus, Pholiderpeton, and Pteroplax), Scotland (Anthracosaurus, Palaeoherpeton, Pholiderpeton, and Proterogyrinus), Joggins (Calligenethlon), and Florence (Carbonoherpeton) of Nova Scotia, Ohio (Leptophractus and Neopteroplax), and West Virginia (Proterogyrinus), USA; early Permian localities include Texas and Oklahoma, USA (Archeria), and Inta, Russia (Aversor); late Permian locality includes Shanxi, China (Seroherpeton). The green color represents the estimated range of tropical forests. All ages and localities except for Seroherpeton come from the literature (Clack, 1987, 2012; Cope, 1873; Gubin, 1985; Holmes, 1984, 1989; Holmes and Carroll, 2010; Panchen, 1964, 1977). The paleographic maps were modified from Tabor and Poulsen (2008, fig. 3).
Figure 3 in The youngest occurrence of embolomeres (Tetrapoda: Anthracosauria) from the Sunjiagou Formation (Lopingian, Permian) of North China
Figure 3. Holotype of Seroherpeton yangquanensis: photo (a) and line drawing (b) in ventral view. Scale bar equals 50 mm. For abbreviations see Fig. 2.
Fig. 4 in Habitat requirements and occurrence of Crematogaster pilosa (Hymenoptera: Formicidae) ants within intertidal salt marshes
Fig. 4. Logistic regression model (P = 0.03) of the probability of Crematogaster pilosa as a function of brown leaf density between 0.61 and 1.20 m. Stars indicate plots containing ants, and open symbols indicate plots not containing ants. Vertical dashed line represents a 50% probability of ants and occurs at a brown leaf density of 2.5 m−1, which equals 1.5 brown leaves between 0.61 and 1.20 m above the marsh surface.
Fig. 2 in Habitat requirements and occurrence of Crematogaster pilosa (Hymenoptera: Formicidae) ants within intertidal salt marshes
Fig. 2. Mean vegetation heights for marsh plots containing ants (n = 8) and plots not containing ants classified by their dominant vegetation type: short (n = 7) and tall (n = 2). All plots were from Dean Creek and Odum's Marsh. Mean heights are the weighted average of all vegetation counts within plots. Letters above whiskers signify significant difference using Tukey's HSD with P <0.05.
Fig. 1 in Habitat requirements and occurrence of Crematogaster pilosa (Hymenoptera: Formicidae) ants within intertidal salt marshes
Fig. 1. Southern tip of Sapelo Island, Georgia (USA). Location of Crematogaster pilosa observations and vegetation assessments in Odum's Marsh (A) and Dean Creek (C). Presence/absence of ants along Lighthouse Creek (B) from canoe and baited trap survey. Sites containing C. pilosa were labeled "ants", those not containing ants were labeled by their vegetation (i.e., short or tall) based on maximum vegetation height.
Fig. 3 in Habitat requirements and occurrence of Crematogaster pilosa (Hymenoptera: Formicidae) ants within intertidal salt marshes
Fig. 3. Height-specific vegetation density for marsh plots with and without ants in Dean Creek and Odum's Marsh. Vegetation density is the number of vegetation features (i.e., stems and leaves) per vertical meter above an average point on the marsh surface. Integrating vertically produces the average number of vegetation features above a single point. All plots containing Crematogaster pilosa were grouped (ants); plots not containing ants were classified by the maximum vegetation height of Spartina alterniflora (i.e., tall or short). Vegetation density distributions are the means for tall (n = 2), ants (n = 8), and short (n = 7) plots.
Fig. 1 in Occurrence of Anastrepha fraterculus and Ceratitis capitata (Diptera: Tephritidae) in organically grown Rubus (Rosales: Rosaceae), in two contrasting environments of northwestern Argentina
Fig. 1. Precipitation (P), evapotranspiration (ET), and hydric balance (HB = P − ET) near Monte Grande (27.0000°S, 65.4000°W; 350 m altitude; Tucumán, Argentina) in 2013 (A) and 2014 (B).
Fig. 2 in Short communication On the occurrence of the invasive Atlantic blue crab Callinectes sapidus Rathbun 1896 (Decapoda: Brachyura: Portunidae) in Sicilian inland waters
Fig. 2 - Neighbor-Joining tree based on a 659-bp long fragment of the mtDNA COI gene of Callinectes sapidus using Kimura-2- parameter distance model. The different clades are coloured according to their lineage as described by Windsor et al., 2019: clear blue, Lineage 1 (northwestern Atlantic and Gulf of Mexico); pink, Lineage 2 (Caribbean region); orange, Lineage 3 (Brazil). Novel sequences are reported in bold. The analysed specimens are reported using the GenBank® Accession numbers listed also in Table S1. / Albero Neighbor-Joining basato su un frammento lungo 659-pb del gene mtDNA COI di Callinectes sapidus, utilizzando il modello di distanza "Kimura-2-parameter". I diversi cladi sono colorati secondo il loro lignaggio come descritto da Windsor et al., 2019: blu chiaro, "Lineage 1" (Atlantico nord-occidentale e Golfo del Messico); rosa, "Lineage 2" (regione caraibica); arancione, "Lineage 3" (Brasile). Le sequenze nuove sono riportate in grassetto. Gli esemplari analizzati sono riportati utilizzando i numeri di accesso Gen- Bank® elencati anche nella Tabella S1.
Fig. 1 in Short communication On the occurrence of the invasive Atlantic blue crab Callinectes sapidus Rathbun 1896 (Decapoda: Brachyura: Portunidae) in Sicilian inland waters
Fig. 1 - Location of the sampling sites. Red circles indicate the new Sicilian sites where Callinectes sapidus (inbox) was sampled; 1) Imera Meridionale river. 2) Irminio river. White circles indicate previous records of the species (see Mancinelli et al., 2021 for further information). / Localizzazione dei siti campionati. I cerchi rossi indicano i nuovi siti siciliani dove è stato campionato Callinectes sapidus (nel riquadro); 1) fiume Imera Meridionale. 2) fiume Irminio. I cerchi bianchi indicano precedenti record della specie (vedi Mancinelli et al., 2021 per ulteriori informazioni).
Fig. 4 in Occurrence and seasonality of internal parasite infection in elephants, Loxodonta africana, in the Okavango Delta, Botswana
Fig. 4. The prevalence of fluke (= trematode) eggs in wild elephants of different ages, using sedimentation of FP-samples (formalin-preserved faecal samples).
Fig. 2 in Occurrence and seasonality of internal parasite infection in elephants, Loxodonta africana, in the Okavango Delta, Botswana
Fig. 2. Nematode egg densities found in UP-samples (unpreserved, immediately analysed faecal samples) from wild elephants, categorised into two group types. Group 1 consists of groups with all female elephants and/or male elephants under the age of 15 years, and Group 2 consists of male elephants aged 15 years or more. Error bars show the standard deviation. EPG = eggs per gram of faeces.
Fig. 1 in Occurrence and seasonality of internal parasite infection in elephants, Loxodonta africana, in the Okavango Delta, Botswana
Fig. 1. The prevalence of coccidial oocysts in FP-samples (formalin-preserved faecal samples) from wild elephants, in each month (2008 to 2012 combined).
Fig. 3 in Occurrence and seasonality of internal parasite infection in elephants, Loxodonta africana, in the Okavango Delta, Botswana
Fig. 3. Photomicrographs of typical nematode (A) and trematode (= fluke, B) eggs found in elephant faecal samples. For dimensions see text.
Fig. 1 in The occurrence of taeniids of wolves in Liguria (northern Italy)
Fig. 1. Study area, Liguria (Italy). Dark areas represent transects investigated to sample wolf scats. Each square represents a sample unit of 100 km2 over an area of 5343 km2.
Fig. 2. Giardia duodenalis 18S in Giardia duodenalis and Cryptosporidium occurrence in Australian sea lions (Neophoca cinerea) exposed to varied levels of human interaction
Fig. 2. Giardia duodenalis 18S rRNA phylogenetic tree. Phylogenetic analysis of Giardia duodenalis positive samples was performed using a fragment of 18S rRNA gene. Analysis within the phylogenetic framework placed sea lion samples within the assemblage B (n = 27) and assemblage A clades (n = 1). Branch values indicate percent bootstrapping using 1000 replicates.
Fig. 1 in Giardia duodenalis and Cryptosporidium occurrence in Australian sea lions (Neophoca cinerea) exposed to varied levels of human interaction
Fig. 1. (A) Western Australia sampling locations. Faecal samples were collected from West Australia Sea lion colonies on Beagle and North Fisherman Islands. Coastal settlements and human impacted camping locations within close proximity to Sea lion colonies are indicated. (B) South Australia sampling locations. Australian sea lion faecal samples were collected from South Australia colonies; Blefuscu, Lewis, Liguanea, Lilliput, Olive and West Waldegrave Islands. Coastal towns and camping areas within close proximity to Australian Sea lion colonies are identified. (C) South Australia sampling locations: Kangaroo Island. Three colonies were sampled from Kangaroo Island including Cape Gantheaume, Seal Bay and Seal Slide. Coastal towns and recreational beach camping sites on the island are indicated.
Fig. 5 in Occurrence Download
Fig. 5. Occurrence records of Taiwan whistling thrushes in the Taipei city. The occurrence data are downloaded from the Global Biodiversity Information Facility database (GBIF.org, 15th December 2018, https://doi.org/10.15468/dl.svzckk). The records for the central and non-central areas of the Taipei city from 1996 to 2016 are shown.
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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)
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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.