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56 results for “Caretta caretta”
Fig. 8 in SYNOPSIS OF THE BIOLOGICAL DATA ON THE LOGGERHEAD SEA TURTLE CARETTA CARETTA (LINNAEUS 1758)
Fig. 8. Growth rates for loggerheads during the first year of activity. Figure from Frazer (1982). (%¼) Meanfrom Kaufmann (1967); (V) Mean from Caldwell et al. (1955); (•) Grand mean from Stickney et al. (1973);) (O) Mean from Rebel (1974); (%) Mean from Witham and Futch (1977).
Fig. 5 in SYNOPSIS OF THE BIOLOGICAL DATA ON THE LOGGERHEAD SEA TURTLE CARETTA CARETTA (LINNAEUS 1758)
Fig. 5. Worldwide nesting locations of the loggerhead. Stars represent major nesting locations arid circles indicate minor nesting areas.
Fig. 7 in SYNOPSIS OF THE BIOLOGICAL DATA ON THE LOGGERHEAD SEA TURTLE CARETTA CARETTA (LINNAEUS 1758)
Fig. 7. Histogram showing size frequency distribution of loggerheads stranded along European coasts of the Atlantic Ocean (Brongersma 1972).
Fig. 6 in SYNOPSIS OF THE BIOLOGICAL DATA ON THE LOGGERHEAD SEA TURTLE CARETTA CARETTA (LINNAEUS 1758)
Fig. 6. Nesting locations of the loggerhead in the west-central Atlantic Ocean and Caribbean Sea. Heavy stippling represents major areas of nesting; light stippling represents areas of lesser but still important nesting concentrations; arrows represent areas with sporadic but consistent nesting, or areas where loggerheads have nested only rarely.
Fig. 9 in SYNOPSIS OF THE BIOLOGICAL DATA ON THE LOGGERHEAD SEA TURTLE CARETTA CARETTA (LINNAEUS 1758)
Fig. 9. Growth rates for loggerheads beyond the first year in captivity. Figure from Frazer (1982). (%) Calculated from Uchida(1967); (O) Data for Parker's (1929) fastestgrowing turtle; (•) Mean for three other turtles of Parker's (1929); (V) Mean from Hildebrand and Hatsel (1927); (%¡) Mean from Hughes et al. (1967); (%¼) Grand mean from Schwartz (1981).
Fig. 3. A-C in SYNOPSIS OF THE BIOLOGICAL DATA ON THE LOGGERHEAD SEA TURTLE CARETTA CARETTA (LINNAEUS 1758)
Fig. 3. A-C Dorsal, ventral, and lateral views of skull of adult male loggerhead (100 cm CL) from Sanibel Island, FL (Pritchard and Trebbau 1984).
Fig. 1 in Seasonal residency of loggerhead turtles Caretta caretta tracked from the Gulf of Manfredonia, South Adriatic Abstract
Fig. 1: Positions and paths of four loggerhead turtles (A, B, D, E) which remained in the Gulf of Manfredonia during the monitored period. The grey areas represent KDE 50%. Isobaths are shown (10, 20, 50 m).
Fig. 2 in Seasonal residency of loggerhead turtles Caretta caretta tracked from the Gulf of Manfredonia, South Adriatic Abstract
Fig. 2: Turtle C. (a) entire path.(b) coastal subarea of the periods 4 Jul-11 Nov 2012 and 3 May-27 Jun 2013, where the grey area represents KDE 50% for aggregated data. (c)the same subarea with separate KDE 50% for the period 2012 (grey area) and 2013 (ellipse). AL: Albania; BA: Bosnia and Herzegovina; HR: Croatia; ME: Montenegro. Isobaths 200m (a) and 20 m (b and c) are shown.
Figure 1 in Reproductive and ecological similarity between Caretta caretta (Linnaeus, 1758) and Eretmochelys imbricata (Linnaeus, 1766) in southern Bahia (Brazil)
Figure 1. Location of the study area on the Brazilian coast. The river mouth corresponds to the Tijuípe River (Bahia, Brazil).
Figure 3 in Reproductive and ecological similarity between Caretta caretta (Linnaeus, 1758) and Eretmochelys imbricata (Linnaeus, 1766) in southern Bahia (Brazil)
Figure 3. Similarity of hatchlings between species. a = Caretta caretta and x = Eretmochelys imbricata. The numbers and red circles highlight the three groups of ecological similarity among hatchlings.
Figure 6 in Reproductive and ecological similarity between Caretta caretta (Linnaeus, 1758) and Eretmochelys imbricata (Linnaeus, 1766) in southern Bahia (Brazil)
Figure 6. Correlation between the hatch response of (A) Eretmochelys imbricata and (B) Caretta caretta and temperature.
Figure 2 in Reproductive and ecological similarity between Caretta caretta (Linnaeus, 1758) and Eretmochelys imbricata (Linnaeus, 1766) in southern Bahia (Brazil)
Figure 2. Correlation between the number of nests observed for the Caretta caretta and Eretmochelys imbricata. The descending line shows the correlation pattern. The number of nests ranged from 0 to 3 for each sample (n=102).
Figure 2 in Nesting activity of sea turtles, Caretta caretta (Linnaeus, 1758) and Chelonia mydas (Linnaeus, 1758) (Reptilia, Cheloniidae), at Patara Beach (Antalya, Turkey) over four nesting seasons
Figure 2. Population trend of sea turtles expressed in number of nests at Patara Beach over 20 seasons (given in Table 3).
Figure 1 in Nesting activity of sea turtles, Caretta caretta (Linnaeus, 1758) and Chelonia mydas (Linnaeus, 1758) (Reptilia, Cheloniidae), at Patara Beach (Antalya, Turkey) over four nesting seasons
Figure 1. Temporal distribution of nests in four nesting seasons (2010, 2012, 2013, and 2014) at Patara Beach.
Figure 1 in Invertebrate infestation in green turtle (Chelonia mydas (Linnaeus, 1758)) and loggerhead turtle (Caretta caretta (Linnaeus, 1758)) nests on Alata Beach, Mersin, Turkey
Figure 1. The important sea turtle nesting beaches in Turkey and a general view of Alata beach showing the back structure.
Assessment of the nesting population demography of loggerhead turtles (Caretta caretta) in La Roche Percée: first long-term monitoring in New Caledonia.
<p><span>Population monitoring is essential to assess, manage and protect threatened species. Although the South Pacific loggerhead turtle subpopulation is classified as critically endangered by the IUCN, monitoring data are scarce. </span></p> <p><span>This study reports the results of the first long-term monitoring of the nesting population of loggerhead turtles held by Bwärä Tortues Marines on La Roche Percée beach, New Caledonia. </span><span>From 2006 to 2020, Capture Mark Recapture was used to identify nesting individuals. Time and nesting success were recorded on site.</span></p> <p><span>A total of 452 different females were observed and tagged over 14 years. The number of different nesting individuals observed each year showed a significant increase along the timeframe of the study. A remigration interval of 3.34 years was observed and the overall nesting success was 59.02%. This study also reports the inter-nesting intervals, monthly and hourly variabilities in the visits at the nesting site.</span></p> <p><span>The conservation actions led by Bwärä Tortues Marines seem to be correlated with a higher nesting success. This study provides encouraging results and highlights the need to pursue the monitoring and conservation actions implemented by Bwärä Tortues Marines. Further management recommendations are also provided.</span></p>
Assessment of the nesting population demography of loggerhead turtles (Caretta caretta) in La Roche Percée: first long-term monitoring in New Caledonia.
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Fig. 2 in SYNOPSIS OF THE BIOLOGICAL DATA ON THE LOGGERHEAD SEA TURTLE CARETTA CARETTA (LINNAEUS 1758)
Fig. 2. Ventral view of plastron of adult loggerhead (Pritchard and Trebbau 1984).
Fig. 4 in SYNOPSIS OF THE BIOLOGICAL DATA ON THE LOGGERHEAD SEA TURTLE CARETTA CARETTA (LINNAEUS 1758)
Fig. 4. Forearm of adult loggerhead (Romer 1956).
Fig. 1 in SYNOPSIS OF THE BIOLOGICAL DATA ON THE LOGGERHEAD SEA TURTLE CARETTA CARETTA (LINNAEUS 1758)
Fig. 1. Dorsal view of carapace of adult loggerhead (Deraniyagala 1939).
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International Brain Laboratory public data
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OpenNeuro
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