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Fig. 6 in Camallanid nematodes from Clarias gariepinus (Burchell, 1822) in the Crocodile River, Gauteng, South Africa: Exploring diversity and divergence in an acid-mine drainage impacted environment
Fig. 6. Phylogram of Camallanidae based on 18S rDNA, with Spirocerca lupi (Rudolphi, 1809) as the outgroup. Procamallanus and Paracamallanus data from the present study are indicated in purple and orange, respectively. Nodal support presented for Bayesian inference and Maximum Likelihood approaches (BI/ML), with support lower than 0.75/75% excluded and support above 0.9/90% indicated by an asterisk (*).
Fig. 4 in Camallanid nematodes from Clarias gariepinus (Burchell, 1822) in the Crocodile River, Gauteng, South Africa: Exploring diversity and divergence in an acid-mine drainage impacted environment
Fig. 4. Scanning electron micrographs of Paracamallanus cyathopharynx (Baylis, 1923) from Clarias gariepinus (Burchell, 1822). A-anterior end, apical view; B- anterior end, apical view, arrow shows oesophagus; C- isolated buccal capsule, lateral view, arrow shows oesophagus; C(i)- isolated buccal capsule, lateral view, double arrow shows isthmus; D-microdissected anterior buccal capsule, ventral view of longitudinal ridges. E- lateral view of deirid; F, G, G(i)- posterior end of female, apical view, digit-like processes. a = amphid; s = submedian papilla; sc = sclerotised plate; t = trident; 1 = anterior buccal capsule; 2 = anterior part of posterior buccal capsule; 3 = posterior part of buccal capsule.
Fig. 1. Maps indicating the sampling locality within South Africa. A in Camallanid nematodes from Clarias gariepinus (Burchell, 1822) in the Crocodile River, Gauteng, South Africa: Exploring diversity and divergence in an acid-mine drainage impacted environment
Fig. 1. Maps indicating the sampling locality within South Africa. A- Map of Africa. B- Map of South Africa; red square highlighting area of interest. C- Map of Crocodile River flowing from Lake Heritage (sampling site) to Hartbeespoort Dam further downstream.
Fig. 2 in High prevalence rates of Toxoplasma gondii in cat-hunted small mammals - Evidence for parasite induced behavioural manipulation in the natural environment?
Fig. 2. Immunohistochemical stained histological section of the heart of a European water vole (Arvicola amphibius s.l.) (ID B42) showing a T. gondii tissue cyst measuring ~20 μm.
Fig. 1 in High prevalence rates of Toxoplasma gondii in cat-hunted small mammals - Evidence for parasite induced behavioural manipulation in the natural environment?
Fig. 1. Spatial distribution of cat-hunted and trap-captured small mammals in Switzerland Map of Switzerland showing the number of sampled small mammals in each location and the distribution of the different groups used in the study. Groups 1–3: "cat-hunted"; Group 4 ′′trap-captured".
FIGURE 2 in Population genetics of three threatened catfish species in heterogeneous environments of the Cauca River, Colombia
FIGURE 2 | Population structure suggested by STRUCTURE (A–C) and the Discriminant Analysis of the Principal Components (D–F) for Pimelodus grosskopfii (A, D), Sorubim cuspicaudus (B, E), and Ageneiosus pardalis (C, F).
FIGURE 1 in Population genetics of three threatened catfish species in heterogeneous environments of the Cauca River, Colombia
FIGURE 1 | Location of sampling sites of Pimelodus grosskopfii, Sorubim cuspicaudus, and Ageneiosus pardalis in the middle and lower sections of the Cauca River.
Fig. 5 in Trophic strategy of Atlantirivulus riograndensis (Cyprinodontiformes: Rivulidae), a non-annual rivulid threatened by extinction, in a perennial environment, Brazil)
Fig. 5. Seasonal distribution of Atlantirivulus riograndensis by frequency of standard length (SL). Individuals collected at the Banhado dos Pachecos wildlife refuge, Viamão, Rio Grande do Sul, Brazil, in 2012.
Fig. 3 in Trophic strategy of Atlantirivulus riograndensis (Cyprinodontiformes: Rivulidae), a non-annual rivulid threatened by extinction, in a perennial environment, Brazil)
Fig. 3. Index of stomach fullness in relation to standard length. Ontogenetic analysis of the Atlantirivulus riograndensis feeding intensity by sex, collected the Banhado dos Pachecos wildlife refuge, in the city of Viamão, Rio Grande do Sul, Brazil, in 2012.
Fig. 2 in Trophic strategy of Atlantirivulus riograndensis (Cyprinodontiformes: Rivulidae), a non-annual rivulid threatened by extinction, in a perennial environment, Brazil)
Fig. 2. Sampling area of Atlantirivulus riograndensis. Evidence of seasonal modification of landscape at the collection point at Banhado dos Pachecos wildlife refuge, Viamão, Rio Grande do Sul, Brazil, during the year 2012 (a) Summer in March; Autumn in (b) May and (c) in June; (d) Winter in September; Spring in (e) October and (f) November.
Fig. 1 in Trophic strategy of Atlantirivulus riograndensis (Cyprinodontiformes: Rivulidae), a non-annual rivulid threatened by extinction, in a perennial environment, Brazil)
Fig. 1. Geographic location of the capture area of Atlantirivulus riograndensis. Geographical representation of South America, especially (a) Brazilian territory, (b) the state of Rio Grande do Sul and (c) Banhado dos Pachecos wildlife refuge in the city of Viamão, sampling area of Atlantirivulus riograndensis in 2012.
Fig. 4 in Trophic strategy of Atlantirivulus riograndensis (Cyprinodontiformes: Rivulidae), a non-annual rivulid threatened by extinction, in a perennial environment, Brazil)
Fig. 4. Canonical Correspondence Analysis (CCA) of food composition of Atlantirivulus riograndensis representing the importance of seasonal and ontogenetic variables, with p <0:05, according to the length of arrows associated with each vector. Individuals collected at the Banado dos Pachecos wildlife refuge, Viamão, Rio Grande do Sul, Brazil, in 2012. A: ≤ 21.6 mm Standard length; B: Standard length from 21.7 to 32.6 mm; C: Standard length ≥ 32.7 mm.
FIGURE 5 in Bessarabian (Tortonian, Late Miocene) fish otoliths from a transitional freshwater-brackish environment of Mykhailivka, Southern Ukraine
FIGURE 5. Recent otoliths of the genus Neogobius. 1-2, Neogobius melanostomus (Pallas, 1814): ZMMU, P.23515 3, SL91, 43°38'N-51°08'E, inner face (1), dorsal view (2). 3-4, Neogobius pallasi (Berg, 1916): ZMMU, P.23514, SL93, 43°28'N-51°18'E., inner face (3), dorsal view (4). 5-6, Neogobius fluviatilis (Pallas, 1814): ZMMU, P.22433, SL81, 45°20'N-28°57'E, inner face (5), dorsal view (6). 7-9, Neogobius caspius (Eichwald, 1831): 7-8, ZMMU, P.22622 1, SL90, 51°25'N-46°03'E, inner face (7), dorsal view (8); 9, ZMMU, P.22622 2, SL105, 51°25'N-46°03'E, inner face.
FIGURE 4. Otoliths from the Sarmatian s.l in Bessarabian (Tortonian, Late Miocene) fish otoliths from a transitional freshwater-brackish environment of Mykhailivka, Southern Ukraine
FIGURE 4. Otoliths from the Sarmatian s.l. of the Mykhailivka 1. 1-9, Neogobius bettinae n. sp.: NMNHU-P 33/1497 (paratype), inner face (1); NMNHU-P 33/1498 (paratype), inner face (2); NMNHU-P 33/1499 (paratype), inner face (3), ventral view (4); NMNHU-P 33/1496 (holotype), inner face (5), ventral view (6); NMNHU-P 33/1500 (paratype), inner face (7), ventral view (8); NMNHU-P 33/1501 (paratype), inner face (9). 10-19, Neogobius rhachis Rückert-Ülkümen, 1993 in Rückert-Ülkümen et al., 1993: NMNHU-P 33/1504, inner face (10), ventral view (11); NMNHU-P 33/1505, inner face (12), ventral view (13); NMNHU-P 33/1506, inner face (14), ventral view (15); NMNHU-P 33/1507, inner face (16), ventral view (17); NMNHU-P 33/1508, inner face (18); NMNHU-P 33/1509, inner face (19). Scale bars equal 1 mm. 5- 8, 10, 11, 14, 15, 18 are mirrored.
FIGURE 2 in Bessarabian (Tortonian, Late Miocene) fish otoliths from a transitional freshwater-brackish environment of Mykhailivka, Southern Ukraine
FIGURE 2. Stratigraphical position of the Mykhailivka section. Lithological and paleontological data from Prisyazhniuk et al. (2006). Reconstruction of environmental log deduced from Prisyazhniuk et al. (2006).
FIGURE 3. Otoliths from the Sarmatian s.l in Bessarabian (Tortonian, Late Miocene) fish otoliths from a transitional freshwater-brackish environment of Mykhailivka, Southern Ukraine
FIGURE 3. Otoliths from the Sarmatian s.l. of the Mykhailivka 1. 1-4, Morone cf. nobilis (Koken, 1891): NMNHU-P 33/ 1482, inner face (1), ventral view (2); NMNHU-P 33/1483, inner face (3), ventral view (4). 5-8, Genyonemus? sp.: NMNHU-P 33/1485, inner face (5), ventral view (6); NMNHU-P 33/1512, inner face (7), ventral view (8). 9-18, Ponticola dorsorostralis (Weinfurter, 1954): NMNHU-P 33/1486, inner face (9), ventral view (10); NMNHU-P 33/1487, inner face (11), ventral view (12); NMNHU-P 33/1488, inner face (13), ventral view (14); NMNHU-P 33/1489, inner face (15); NMNHU-P 33/1490, inner face (16); NMNHU-P 33/1491, inner face (17); NMNHU-P 33/1492, inner face (18). Scale bars equal 1 mm. 5-10, 17, 18 are mirrored.
FIGURE 1 in Bessarabian (Tortonian, Late Miocene) fish otoliths from a transitional freshwater-brackish environment of Mykhailivka, Southern Ukraine
FIGURE 1. Map of Ukraine with the coastline of Eastern Paratethys (blue line) during the late middle Sarmatian s.l. (according to Popov et al., 2004) (1), enlargered part of the lower reaches of the Pivdennyi Buh River (2), location map of the Mykhailivka quarry (3). The Mykhailivka locality is marked by an asterisk.
Figure 1 in Ecological impact and population status of non-native bees in a Brazilian urban environment
Figure 1 Bipartite network and non-native bees sampled in Curitiba. a) Bipartite network, non-native plant and bees colored, b) Anthidium manicatum, female; c) Distributional range of A. manicatum (SpeciesLink); d) Melipona scutellaris worker on Calliandra brevipes; e) Distributional range of M. scutellaris (SpeciesLink), natural records in green.
Fig. 2 in LED grow lights alter sorghum growth and sugarcane aphid (Hemiptera: Aphididae) plant interactions in a controlled environment
Fig. 2. Growth characteristics of grain sorghum grown under conventional lighting (A) from within an environmental chamber, fitted with a W2238 LED grow panel (B and C, see Fig. 1 for light spectrum measured), and for sorghum cv MORHC 858, DKS 37-07, TX 2783, and WSH117 afer 21 d in a growth chamber fitted with a W2238 LED grow panel.
Fig. 3 in LED grow lights alter sorghum growth and sugarcane aphid (Hemiptera: Aphididae) plant interactions in a controlled environment
Fig. 3. Number of true leaves on 4 different sorghum entries grown under conventional and LED light sources.
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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.