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FIGURE 6 in A new perspective on the molecular dating of the brown trout complex with an extended phylogeographic information on the species in Serbia
FIGURE 6 Split graph of the Neighbor-Net phylogenetic network analysis of brown trout lineages. The colors of the haplotypes represent different lineages, and the scale bar represents the nucleotide substitutions per site.
FIGURE 4 in A new perspective on the molecular dating of the brown trout complex with an extended phylogeographic information on the species in Serbia
FIGURE 4 Median-joining network of CR mtDNA sequences belonging to Danubian haplogroups. Haplotypes are represented by colored circles whose size is proportional to haplotype frequencies detected and taken from the literature (supplementary tables S2 and S3). Haplotypes from this study are bolded and framed. Mutations are represented by hatch marks on the lines connecting the haplotypes. Missing or theoretical haplotypes are shown as black dots. The maps show the distribution of haplotypes from the network (A – DA-ES haplotypes, B – DA-INT haplotypes, C – DA-BS haplotypes), and their numbering corresponds to that in supplementary table S2.
FIGURE 3 in A new perspective on the molecular dating of the brown trout complex with an extended phylogeographic information on the species in Serbia
FIGURE 3 Reconstruction of the sequence evolution in the Danubian lineage. Defining variable nucleotide sites in the control region are all placed nearby in the central part of the control region, between the nucleotide positions 540-550 of our alignment. The 542 G → C transversion defines the split of the DAES + DA-INT and the DA-BS; 541 G → A split of the DA-ES + DA-INT (excluding DaBS9) from the DaBS9 haplotype; and 548 C → T defines the DA-ES.
FIGURE 7 in A new perspective on the molecular dating of the brown trout complex with an extended phylogeographic information on the species in Serbia
FIGURE 7 Fossil and geologically calibrated chronogram of the genus Salmo created with a relaxed clock in BEAST 2. 95% highest posterior density (HPD) intervals are shown as gray bars at the nodes. Calibration points are indicated by arrows. Median node ages are shown as node labels. Time estimates are given in millions of years. Clades, that were a priori treated as monophyletic are indicated with a black star, while a red star indicates the clade, where posterior probability was> 90% only in BEAST analysis.
Fig. 1 in Survival Of Embryos And Larvae Of The Rainbow Trout (Oncorhynchus Mykiss, Walbaum, 1792) Under Influence Of Optical Radiation At Various Temperature Regimes
Fig. 1. Linear dependencies of the probit (logit) effect of the death of rainbow trout larvae in vitro from the logarithm of days of fasting for various types of optical radiation at a temperature of 12 (a), 11 (b), 10 (c), 9 (d), 8(e) ° C.
Рис. 1. Места отΛовов микижи в Хабаровском крае: 1 — о. БоΛьшой Шантар (попуΛяция рек СреΑняя и ОΛенья); 2 — мыс Δжаоре; 3 — р. Чоме; 4 — устье р. Тумнин; 5 — р. Матвеевка in Kamchatka Rainbow Trout (Salmonidae) At The Boundaries Of The Botchinsky Nature Reserve: Invasion Or New Area Data?
Рис. 1. Места отΛовов микижи в Хабаровском крае: 1 — о. БоΛьшой Шантар (попуΛяция рек СреΑняя и ОΛенья); 2 — мыс Δжаоре; 3 — р. Чоме; 4 — устье р. Тумнин; 5 — р. Матвеевка
Figure 4 in The brook trout Salvelinus fontinalis (Mitchill, 1814) in the Saint-Pierre and Miquelon archipelago: a review
Figure 4. – Ecotypic diversity of brook trout populations in the Saint-Pierre and Miquelon archipelago. A: Life cycle of anadromous and resident freshwater brook trout in the coastal ponds and streams of the archipelago. B: Life cycle of migratory and resident freshwater brook trout in the Mirande system. Green (A) and white (B) arrows show movements in the marine environment (A) or the Grand Étang de Mirande (B). The blue arrows (light and dark) correspond to movements in the rivers/ponds (A) or tributaries of the Mirande (B).
Figure 5 in The brook trout Salvelinus fontinalis (Mitchill, 1814) in the Saint-Pierre and Miquelon archipelago: a review
Figure 5. – Locations of the three hydrographic systems used for the aquaculture project initiated by the Association de Recherche pour le Développement de l'Aquaculture (ARDA) and the Institut Scientifique et Technique des Pêches Maritimes (ISTPM) at the end of the 1980s in Saint-Pierre and Miquelon.
Figure 3 in The brook trout Salvelinus fontinalis (Mitchill, 1814) in the Saint-Pierre and Miquelon archipelago: a review
Figure 3. – Ecotypic diversity of brook trout populations in the Saint-Pierre and Miquelon; two individuals fished in the Mère Durand River (see location in Fig. 1B). Above: anadromous ecotype; Below: resident ecotype (©: Edgard Gustave).
FIGURE 1 in First study of food webs in a large glacial river: the trophic role of invasive trout
FIGURE 1 | Sampling areas in the Santa Cruz River, Argentina. Upstream area corresponds to the locally known "Labyrinth", and Midstream area correspond to "Estancia San Ramon". Map created by the authors, upper picture taken from Google Earth (R).
Figure 1 in Feeding habit of Brown trout (Salmo trutta fario) in upper parts of river Swat, Pakistan
Figure 1. Percentage of N,W, FO and IRI of various diet components. Table 2. GSI and fullness index of various length groups of brown trout.
Figure 4 in The burmese trout Raiamas guttatus (Day, 1870) (Cypriniformes: Cyprinidae) in South Sumatra revealed its southernmost record of its distributional range
Figure 4. Head pattern of R. guttatus showing large mouth and jaw extending backwards far behind eye (Photo: Muhammad Iqbal).
Figure 1 in The burmese trout Raiamas guttatus (Day, 1870) (Cypriniformes: Cyprinidae) in South Sumatra revealed its southernmost record of its distributional range
Figure 1. Map showing the known distribution of R. guttatus in Sumatra, circle is previous known and triangle is recent distribution record.
Figure 2. Blungun River, location where R in The burmese trout Raiamas guttatus (Day, 1870) (Cypriniformes: Cyprinidae) in South Sumatra revealed its southernmost record of its distributional range
Figure 2. Blungun River, location where R. guttatus found in South Sumatra Province (Photo: Muhammad Iqbal).
Figure 1 in Haplotype diversity of brown trout Salmo trutta (L.) in the broader Iron Gate area
Figure 1. Sampling sites on the streams Brnjica (1), Dobrinjska reka (2), Kožica (3), Mala Boljetinska reka (4), Zlatica (5), Porečka reka (6), Rečka reka (7), Vratna (8), and Zamna (9) in the broader Iron Gate area with the position in the Balkan region given in small figure in lower left.
Figure 2 in Haplotype diversity of brown trout Salmo trutta (L.) in the broader Iron Gate area
Figure 2. Relationships between CR haplotypes of brown trout populations in the broader Iron Gate area constructed using maximum likelihood (A) and maximum parsimony (B) methods (numbers at particular branches represent bootstrap probabilities; bootstrap values under 40% are not represented).
Fig. 3 in Call survey indicates rainbow trout farming alters glassfrog community composition in the Andes of Ecuador
Fig. 3. Map of the study area. Inset: Pichincha Province, Ecuador. Main: Blue points indicate non-trout farm sites whereas red points indicate trout farm sites. Yellow line represents the equator (latitude 0).
Fig. 2 in Call survey indicates rainbow trout farming alters glassfrog community composition in the Andes of Ecuador
Fig. 2. Glassfrog species found during surveys. (A) Centrolene heloderma, (B) Centrolene ballux, (C) Esparana prosoblepon, (D) Nymphargus lasgralarias, (E) Centrolene peristictum, (F) Nymphargus grandisonae, (G) Centrolene lynchi, (H) Egg mass from C. ballux. Nymphargus griffithsi was not encountered during the 2017 survey but has been documented at Kathy's creek in 2012 and 2013 (by Jane A. Lyons). Photographs by Dana G. Wessels (A–F) and Timothy J. Krynak (G–H).
Fig. 1 in Call survey indicates rainbow trout farming alters glassfrog community composition in the Andes of Ecuador
Fig. 1. Trout farming in the Mindo region of Ecuador utilizes a flow-through aquaculture technique. Stream water is diverted into tandem raceways/holding reservoirs and then flows through these reservoirs back into the natural stream system. This figure displays a panoramic view of Finca de Jaime's (FJ) set-up. Photograph by Katherine L. Krynak.
Fig. 4 in Call survey indicates rainbow trout farming alters glassfrog community composition in the Andes of Ecuador
Fig. 4. Two-dimensional NMDS ordination of survey sites and glassfrog species based upon presence of frogs audibly documented in 2017 survey conducted in the Mindo region of Ecuador (Stress = 3%). Red points and labels represent glassfrog species; grey points represent trout farms; and black points represent non-trout farms. RSR = Río Santa Rosa, LC = Lucy's Creek, Bcrk = Ballux Creek, KC = Kathy's Creek, M = Michelle's, C = tributary of the Chalguayacu Grande River, 5F = Five Frog Creek, LRSR = Lower Río Santa Rosa, ST = Santa Teresita, FJ = Finca de Jaime, LS = La Sierra, VC = Verdecocha, EP = El Paraíso del Pescador. Trout farms EP, LS, and VC are not included in the analysis because glassfrogs were not observed at these sites. A significant difference in glassfrog community composition between trout farm and non-trout farm sites was indicated by MRPP (delta = 0.59, A = 0.11, P = 0.03). NMDS1 correlated with elevation; NMDS2 correlated with: percent canopy openness, dissolved oxygen (mg/L), total dissolved solids (mg/L), and conductivity (µS).
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Allen Brain Atlas
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International Brain Laboratory public data
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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.