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Fig. 10 in The Ecology And Migrations Of Sea Turtles 8. Tests Of The Developmental Habitat Hypothesis

Fig. 10. Satellite transmission histories of four large subadult Chelonia mydas from Bermuda. Argos locations displayed are the minimum redundant distance (MRD) output of the Douglas Argos filter algorithm. This output includes points that have a consecutive or near-consecutive neighbor within 6 km. Adaptive kernel density percent volume contours, calculated from the MRD dataset, are also displayed. A, Locations (n 5 103) and volume contours for PTT 07665 (70.4 cm SCLmin). B, Locations (n 5 103) and volume contours for PTT 11676 (72.0 cm SCLmin). C, Locations (n 5 141) and volume contours for PTT 11677 (71.8 cm SCLmin). D, Locations (n 5 253) and volume contours for PTT 60810 (70.0 cm SCLmin).

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Fig. 7 in The Ecology And Migrations Of Sea Turtles 8. Tests Of The Developmental Habitat Hypothesis

Fig. 7. Average number of Chelonia mydas caught per set of the entrapment net at Bermuda by month. Mean and one standard deviation are shown for all sets from January 1992–August 2005. Sample size above each bar is for the number of sets made during each month.

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Fig. 8 in The Ecology And Migrations Of Sea Turtles 8. Tests Of The Developmental Habitat Hypothesis

Fig. 8. The number of Chelonia mydas caught at Bermuda per set of the entrapment net as a function of water temperature. Data shown are for 258 samples from January 1992–August 2005.

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Fig. 3. Chactopsis Kraepelin, 1912, habitat. A in Systematic Revision Of The Neotropical Scorpion Genus Chactopsis Kraepelin, 1912 (Chactoidea: Chactidae), With Descriptions Of Two New Genera And Four New Species

Fig. 3. Chactopsis Kraepelin, 1912, habitat. A. Reserva Ducke, Manaus, Amazonas, Brazil, habitat of Chactopsis amazonica Lourenço and Francke, 1986. B. Guacamayo, Tarapoto, San Martín Department, Peru, habitat of Chactopsis chullachaqui, n. sp. C. Tahuayo River, Loreto Department, Peru, habitat of Chactopsis insignis Kraepelin, 1912.

Fig. 5 in The opportunistic feeding and reproduction strategies of the annual fish Cynopoecilus melanotaenia (Cyprinodontiformes: Rivulidae) inhabiting ephemeral habitats on southern Brazil

Fig. 5. Individuals of Cynopoecilus melanotaenia grouped by frequencies (%) of distribution of oocyte diameters (μm), from wetlands between São Gonçalo channel and Pelotas stream, during May and June 2005, and September 2006. Arrows indicate the size in which the oocytes become mature.

Fig. 3 in The opportunistic feeding and reproduction strategies of the annual fish Cynopoecilus melanotaenia (Cyprinodontiformes: Rivulidae) inhabiting ephemeral habitats on southern Brazil

Fig. 3. Diet of males (a) and females (b) of Cynopoecilus melanotaenia from wetlands between São Gonçalo channel and Pelotas stream, during May and June 2005, and September 2006, according to the frequency of occurrence and dominance of food items.

Fig. 2 in The opportunistic feeding and reproduction strategies of the annual fish Cynopoecilus melanotaenia (Cyprinodontiformes: Rivulidae) inhabiting ephemeral habitats on southern Brazil

Fig. 2. Average, standard error and confidence interval (95%) for the lengths of males and females of Cynopoecilus melanotaenia from wetlands between São Gonçalo channel and Pelotas stream, during May and June 2005, and September 2006.

Fig. 1 in The opportunistic feeding and reproduction strategies of the annual fish Cynopoecilus melanotaenia (Cyprinodontiformes: Rivulidae) inhabiting ephemeral habitats on southern Brazil

Fig. 1. Map of study area showing sampling location for Cynopoecilus melanotaenia between the São Gonçalo channel and Pelotas stream, State of Rio Grande do Sul (RS), Brazil.

Fig. 4 in The opportunistic feeding and reproduction strategies of the annual fish Cynopoecilus melanotaenia (Cyprinodontiformes: Rivulidae) inhabiting ephemeral habitats on southern Brazil

Fig. 4. Linear regressions between total length (TL) and total weight (TW) of males (open symbol, dotted line) and females (black symbol, solid line) of Cynopoecilus melanotaenia from wetlands between São Gonçalo channel and Pelotas stream, during May and June 2005, and September 2006. ln (TW) = 2.63 ln (TL) - males 10.41, R2 = 0.82; ln (TW) = 3.92 ln (TL) - 14.49, R2 = 0.87.

Fig. 4 in Diet and feeding strategy of the dusky grouper Mycteroperca marginata (Actinopterygii: Epinephelidae) in a man-made rocky habitat in southern Brazil

Fig. 4. Feeding strategy diagram for individuals of three size classes (A: <400 mm TL; B: 400-500 mm TL; C:>500 mm TL) of the dusky grouper Mycteroperca marginata. Prey-specific abundance plotted against frequency of occurrence of food items in the diet of the dusky grouper. The inserted boxed (A) represents a conceptual diagram of a resource niche width characterized by a high between-phenotype component (sensu Amundsen et al., 1996) to niche width contribution. The number of individuals analyzed in each size class is 29, 34 and 15, respectively.

Fig. 3 in Diet and feeding strategy of the dusky grouper Mycteroperca marginata (Actinopterygii: Epinephelidae) in a man-made rocky habitat in southern Brazil

Fig. 3. Average values (±SD) of prey's size (mm, TL) and biomass (g) in the stomach content of three size classes (<400 mm TL; 400-500 mm TL;>500 mm TL) of the dusky grouper Mycteroperca marginata. The number of individuals analyzed in each size class is 29, 34 and 15, respectively.

Fig. 1 in Diet and feeding strategy of the dusky grouper Mycteroperca marginata (Actinopterygii: Epinephelidae) in a man-made rocky habitat in southern Brazil

Fig. 1. Patos Lagoon (10.360 km2) in southern Brazil (A) and the 4.5 km long pair of jetties that connects the estuarine zone of the lagoon with the Atlantic Ocean (B), detail of the west jetty and their large pieces of rock nearly 10 ton each (C). These rocky jetties are located in the Rio Grande City (Rio Grande do Sul State) in southern Brazil.

Fig. 2 in Diet and feeding strategy of the dusky grouper Mycteroperca marginata (Actinopterygii: Epinephelidae) in a man-made rocky habitat in southern Brazil

Fig. 2. Components (%N, %W, %F) of the Index of Relative Importance (%IRI) for each of the five major categories of food found in the stomach content of three size classes (A: <400 mm TL; B: 400-500 mm TL; C:>500 mm TL) of the dusky grouper Mycteroperca marginata. The number of individuals analyzed in each size class is 29, 34 and 15, respectively. Mollusks did not occur in the larger size class (> 500 mm TL).

Fig. 2 in Habitat simplification affects nuclear-follower foraging association among stream fishes

Fig. 2. General view of the altered (a) and unaltered (b) sites in the córrego Olho d'Água, Central-West Brazil. Photos: Renato M. Romero and Fabrício B. Teresa.

Fig. 1 in Habitat simplification affects nuclear-follower foraging association among stream fishes

Fig. 1. Location of the study area, indicating the córrego Olho d'Água in South America (black dot).

Fig. 3 in Spatial pattern of a fish assemblage in a seasonal tropical wetland: effects of habitat, herbaceous plant biomass, water depth, and distance from species sources

Fig. 3. Partial regressions testing the effects of water depth (left) and distance from colonizing source (right) on fish species richness collected in 22 plots in Site of Long-Term Sampling (SLTS). Only statistically significant relationships are shown.

Fig. 3 in Habitat partitioning, habits and convergence among coastal nektonic fish species from the São Sebastião Channel, southeastern Brazil

Fig. 3. Dendrogram of ecomorphological relationships (similarity) for the 17 nektonic fish species studied. Cluster analysis is by the Euclidean distance measure and Group Average linkage method using the same scores (i.e., coordinates) calculated for PCA and plotted in Fig. 2 (cophenetic coefficient r = 0.86). Anc tri = Anchoa tricolor; Ath bra = Atherinella brasiliensis; Car lat = Caranx latus; Chl chr = Chloroscombrus chrysurus; Fis tab = Fistularia tabacaria; Har jag = Harengula jaguana; Hyp uni = Hyporhamphus unifasciatus; Lag lae = Lagocephalus laevigatus; Mug cur = Mugil curema; Oli sau = Oligoplites saurus; Pom sal = Pomatomus saltatrix; Sar jan = Sardinella janeiro; Sco bra = Scomberomorus brasiliensis; Sel vom = Selene vomer; Str tim = Strongylura timucu; Tra car = Trachinotus carolinus; Tri lep = Trichiurus lepturus. There is no scale among the fishes (see Table 2 for standard length range) (illustrations: Alexandre C. Ribeiro).

Fig. 2 in Habitat partitioning, habits and convergence among coastal nektonic fish species from the São Sebastião Channel, southeastern Brazil

Fig. 2. Distribution of the 17 nektonic fish species in ecomorphological space. Ordination is by the first two axes of PCA (cumulative % of variance = 73) (see Table 5). Anc tri = Anchoa tricolor; Ath bra = Atherinella brasiliensis; Car lat = Caranx latus; Chl chr = Chloroscombrus chrysurus; Fis tab = Fistularia tabacaria; Har jag = Harengula jaguana; Hyp uni = Hyporhamphus unifasciatus; Lag lae = Lagocephalus laevigatus; Mug cur = Mugil curema; Oli sau = Oligoplites saurus; Pom sal = Pomatomus saltatrix; Sar jan = Sardinella janeiro; Sco bra = Scomberomorus brasiliensis; Sel vom = Selene vomer; Str tim = Strongylura timucu; Tra car = Trachinotus carolinus; Tri lep = Trichiurus lepturus. There is no scale among the fishes (see Table 2 for standard length range) (illustrations: Alexandre C. Ribeiro).

Fig. 1 in Spatial pattern of a fish assemblage in a seasonal tropical wetland: effects of habitat, herbaceous plant biomass, water depth, and distance from species sources

Fig. 1. Geographical location of the study area and the Site of Long-Term Sampling (in the area). The system is installed in the Pantanal, Brazil.

Fig. 1 in Habitat partitioning, habits and convergence among coastal nektonic fish species from the São Sebastião Channel, southeastern Brazil

Fig. 1. Map indicating the location of the study area (São Sebastião Channel) and the marine station of the University of São Paulo (CEBIMar-USP) on the coast of São Paulo, southeastern Brazil.