Find research datasets worth reusing

Fig. 2 in Distributions and phylogeographic data of rheophilic freshwater fishes provide evidences on the geographic extension of a central-brazilian amazonian palaeoplateau in the area of the present day Pantanal Wetland

Fig. 2. Distribution of sampled localities for Jupiaba acanthogaster in the upper rio Paraguay, rio Tapajós and rio Xingú basins. The drainages of the rio Tocantins, rio Araguaia and upper rio Paraná are also illustrated. Drainage boundaries delimited by a continuous black line.

Fig. 1 in Distributions and phylogeographic data of rheophilic freshwater fishes provide evidences on the geographic extension of a central-brazilian amazonian palaeoplateau in the area of the present day Pantanal Wetland

Fig. 1. Map of the upper rio Paraguay basin and adjoining areas showing the distribution of Leporinus octomatulatus, Jubiaba acanthogaster, Oligosarcus perdido, Moenkhausia cosmops, and Hypostomus cochliodon, exemplifying distributional pattern discussed in this paper.

Fig. 7 in Longitudinal use of feeding resources and distribution of fish trophic guilds in a coastal Atlantic stream, southern Brazil

Fig. 7. Spearman correlations between the distribution (percentage frequency) of guilds and scores of the first axis of the principal components analysis (PCA1) applied to the correlation matrix of abiotic variables. White circle = headwaters; gray circle = middle stretch; and black circle = mouth of the Vermelho River, East Atlantic basin, Antonina, Paraná State, Brazil.

Fig. 5 in Longitudinal use of feeding resources and distribution of fish trophic guilds in a coastal Atlantic stream, southern Brazil

Fig. 5. Longitudinal niche breadth (B values) of each fish trophic guild in the Vermelho River, East Atlantic basin, Antonina, Paraná State, Brazil. Aq = aquatic; ter = terrestrial.

Fig. 4 in Longitudinal use of feeding resources and distribution of fish trophic guilds in a coastal Atlantic stream, southern Brazil

Fig. 4. Mean ± standard error of diet breadth (B) of fish trophic guilds in the Vermelho River, East Atlantic basin, Antonina, Paraná State, Brazil. Aq = aquatic; ter = terrestrial. Piscivores and omnivores are not included in the ANOVA.

Fig. 6 in Longitudinal use of feeding resources and distribution of fish trophic guilds in a coastal Atlantic stream, southern Brazil

Fig. 6. Density (a) and biomass (b) of trophic guilds along the longitudinal gradient of the Vermelho River, East Atlantic basin, Antonina, Paraná State, Brazil. Aq = aquatic; ter = terrestrial.

Fig. 3 in Longitudinal use of feeding resources and distribution of fish trophic guilds in a coastal Atlantic stream, southern Brazil

Fig. 3. Ordination of fish species in the respective trophic guilds (a, b, c) and food items (d, e, f) along the longitudinal gradient of the Vermelho River, East Atlantic basin, Antonina, Paraná State, Brazil. Circles represent species belonging to the same trophic guild. Codes according to Table 3.

Fig. 2 in Longitudinal use of feeding resources and distribution of fish trophic guilds in a coastal Atlantic stream, southern Brazil

Fig. 2. Ordination of sampling sections along the environmental gradient defined by the first two axes of the principal components analysis (PCA1 and PCA2) applied to the correlation matrix of abiotic variables of the Vermelho River, East Atlantic basin, Antonina, Paraná State, Brazil.

Fig. 1 in Longitudinal use of feeding resources and distribution of fish trophic guilds in a coastal Atlantic stream, southern Brazil

Fig. 1. Location of the Vermelho River, East Atlantic basin, Antonina, Paraná State, Brazil. Black circles indicate the sampling sections; arrow indicates the direction of flow.

Fig. 7 in Habitat Distribution Of Dytiscus Latissimus Linnaeus, 1758 (Coleoptera: Dytiscidae) In The Ecosystem Of Ruģeļi Fish Ponds (Daugavpils, Latvia)

Fig. 7. Distribution of D. latissimus in the ecosystem of RuĢeļi fish ponds (Daugavpils) № 1 - 4 – inspected control sites, where № 3, 4 – water-storage basins Lielo Stropicas and Mazo Stropicas; А – findings of D. latissimus; В – breeding places of D. latissimus.

Fig. 4 in The Distribution Of The Invasive Fish Amur Sleeper, Rotan Perccottus Glenii Dybowski, 1877 (Osteichthyes, Odontobutidae), In Latvia

Fig. 4. Perccottus glenii adult individual from the population in Pond Universitates with the minimum age of 41. 55°52'19.16"N; 26°30'26.14"E. Daugavpils, Latvia, 2015.

Fig. 5 in The Distribution Of The Invasive Fish Amur Sleeper, Rotan Perccottus Glenii Dybowski, 1877 (Osteichthyes, Odontobutidae), In Latvia

Fig. 5. The location of records of Perccottus glenii in Latvia and catchments basins: 1. Sventaja river basin; 2. Bartas-Liepajas lake basin; 3. Saka river basin; 4. Venta river basin; 5. Irve river basin; 6. Lielupe river basin; 7. Nemunas river basin; 8. Daugava river basin; 9. Gauja river basin; 10. Salaca river basin; 11. Emajegi river basin; 12. Veļkaja river basin baseins; 13. Baltic Sea small rivers' basins (the basic map of catchments basins from http://www.upes.lv/k-a-r-t-e/, open access).

Fig. 6. A pond overgrown with dense vegetation – a in The Distribution Of The Invasive Fish Amur Sleeper, Rotan Perccottus Glenii Dybowski, 1877 (Osteichthyes, Odontobutidae), In Latvia

Fig. 6. A pond overgrown with dense vegetation – a typical small pond biotope of Perccottus glenii. Pond Galdnieki, Kalkunes parish, Daugavpils district. 55°50'2.87"N; 26°28'58.57"E.

Fig. 7 in The Distribution Of The Invasive Fish Amur Sleeper, Rotan Perccottus Glenii Dybowski, 1877 (Osteichthyes, Odontobutidae), In Latvia

Fig. 7. The photo from the popular Latvian trade web-site with subadult and young adult of Perccottus glenii for sale with length of 5 – 10 cm. 30 Perccottus glenii ready for selling are seen on the photo (www.ss.lv).

opencc-by-4.0Dec 2023View details →

Figure 2 in AfriBasins: a new framework in FishBase for the analysis of African fresh and brackish water fish distributions, with a discussion on the Congo basin fauna

Figure 2. – Family level composition of the fish fauna of the Congo Basin s.s. "Other" includes the following families: Tetraodontidae, Bagridae, Citharinidae, Dasyatidae, Hepsetidae, Protopteridae, Syngnathidae, Mugilidae, Notopteridae, Channidae, Ariidae, Cynoglossidae, Elopidae, Pristigasteridae, Latidae, Megalopidae, Ophichthidae, Pantodontidae, Phractolaemidae, Pristidae and Carangidae.

opencc-by-4.0Dec 2023View details →

Figure 5 in AfriBasins: a new framework in FishBase for the analysis of African fresh and brackish water fish distributions, with a discussion on the Congo basin fauna

Figure 5. – Cluster analysis on the fish distribution data for the Congo Basin s.s., based on (A) the Ochiai coefficient and (B) the correlation ratio.

opencc-by-4.0Dec 2023View details →

Figure 7 in AfriBasins: a new framework in FishBase for the analysis of African fresh and brackish water fish distributions, with a discussion on the Congo basin fauna

Figure 7. – Evolution of the estimated number of species based on various definitions of the Congo basin: Central Congo, i.e. Kinshasa to Kisangani, without Kasai upstream from Mushie (Poll and Gosse, 1963); without lakes Bangweulu and Mweru (Roberts, 1972); entire Congo (Poll, 1973); excluding Lake Tanganyika (Lowe-McConnell, 1987); excluding lakes Tanganyika and Mweru, primary freshwater species (Teugels and Guégan, 1994); Zaïre, probably only includes primary freshwater species (Lévêque, 1997); Zaïre, probably includes primary, secondary and peripheral species (Lévêque, 1997); Congo River system, at least 700 species (Skelton, 2001); Congo and Lake Tanganyika (Revenga and Kura, 2003); Congo River system (Thieme et al., 2005); the Congo (Dumont, 2009); Congo basin including the Rift Valley region with lakes Tanganyika and Kivu and the Malagarasi basin (Snoeks et al., 2011).

opencc-by-4.0Jan 2015View details →

Fig. 2. Area diagram depicting relationships among the 24 in Biogeography of freshwater fishes from the Northeastern Mata Atlântica freshwater ecoregion: distribution, endemism, and area relationships

Fig. 2. Area diagram depicting relationships among the 24 coastal drainages analyzed, obtained by parsimony analysis of endemicity based on freshwater fishes. The topology represents the strict consensus of five equally parsimonious trees obtained through a heuristic search (length= 71 steps, CI = 0.521, RI = 0.709).

opencc-by-4.0Jan 2015View details →

Fig. 1 in Biogeography of freshwater fishes from the Northeastern Mata Atlântica freshwater ecoregion: distribution, endemism, and area relationships

Fig. 1. Map showing the Northeastern Mata Atlântica ecoregion, the rivers included in the PAE, and the groups recovered from the analysis. Adjacent freshwater ecoregions are: (327) São Francisco, (329) Paraíba do Sul, and (344) Upper Paraná.