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65 results for “Salvator”
Figure 2 in Oxidative and osmotolerant effects in Salvator merianae (Squamata: Teiidae) red blood cells during hibernation
Figure 2. Logarithmic in base 10 values of oxidative biomolecules level for each period collected (n = 6). Wilcox Test: P = 0.31. Sum symbol (+) is the mean and SD are the horizontal lines; median is the vertical line within the boxes and range is distance from the median to the end of the boxes.
Figure 1 in Oxidative and osmotolerant effects in Salvator merianae (Squamata: Teiidae) red blood cells during hibernation
Figure 1. (a) Osmotic fragility in percentage by saline concentration from both periods studied (GLM: F = 2.56, P = 0.03). No statistical differences were observed between individualized pairs of saline concentrations; (b) Overall osmotic fragility difference between periods considering only periods effect (GLM: F = 9.72, P = 0.01) (n = 6). Sum symbol (+) is the mean and SD are the horizontal lines; median is the vertical line within the boxes and range is distance from the median to the end of the boxes.
Figure 3 in Oxidative and osmotolerant effects in Salvator merianae (Squamata: Teiidae) red blood cells during hibernation
Figure 3. Logarithmic in base 10 values of (a) Enzymatic activity level of glutathione peroxidase – GPx and (b) activity of glutathione reductase - GR of red blood cells in hibernation and active periods (n = 6). T-test, P = 0.68 and P = 0.10, respectively. Sum symbol (+) is the mean and SD are the horizontal lines; median is the vertical line within the boxes and range is distance from the median to the end of the boxes.
Fig. 5 in The effect of environmental enrichment on Salvator merianae (Squamata: Teiidae) under captivity conditions
Fig. 5. Representation of the interactions between individuals in each enclosure, R1 and R2, with (R2 WE) and without enrichment (R2 W/O-E) based on the recorded chase and flight events.MWM: male without mark, MWP: male white point, MYP; male yellow point, F: female. Fig. 5. Representación de las interacciones entre individuos en cada recinto, R1 y R2, con (R2 WE) y sin enriquecimiento (R2 W/O-E) en base a los eventos de persecución y huida registrados. MWM: macho sin marca, MWP: macho punto blanco, MYP; punto amarillo macho, F: hembra.
Fig. 3 in The effect of environmental enrichment on Salvator merianae (Squamata: Teiidae) under captivity conditions
Fig. 3. Comparison in the frequency of Reproductive Behavior in Males between R1 and R2 during the 3 months of the experiment. Fig. 3. Comparación en la frecuencia del Comportamiento Reproductivo en Machos entre R1 y R2 durante los 3 meses del experimento.
Fig. 2 in The effect of environmental enrichment on Salvator merianae (Squamata: Teiidae) under captivity conditions
Fig. 2. Comparison of cumulative proportions of behavioral categories in R1 and R2, with and without enrichment (inner circle: females, outer circle: males). Fig. 2. Comparación de proporciones acumuladas de categorías de comportamiento en R1 y R2, con y sin enriquecimiento (círculo interior: mujeres, círculo exterior: hombres).
Fig. 4 in The effect of environmental enrichment on Salvator merianae (Squamata: Teiidae) under captivity conditions
Fig. 4. Tables of sociometric matrices for each enclosure R1 and R2, with (R2 WE) and without enrichment (R2 W/O-E). MWM: male without mark, MWP: male white point, MYP; male yellow point, F: female. Fig. 4. Cuadros de matrices sociométricas para cada recinto R1 y R2, con (R2 WE) y sin enriquecimiento (R2 W/O-E). MWM: macho sin marca, MWP: macho punto blanco, MYP; punto amarillo macho, F: hembra.
Fig. 1 in The effect of environmental enrichment on Salvator merianae (Squamata: Teiidae) under captivity conditions
Fig. 1. Examples of different environmental enrichment activities carried out in the R2. Fig. 1. Ejemplos de diferentes actividades de enriquecimiento ambiental realizadas en el R2.
Figure 4 in Skeletochronology in long tubular bones of the Javan water monitor lizard, Varanus salvator bivittatus in the juvenile stage (Lacertilia: Varanidae)
Figure 4. Cross sections of the diaphysis fibula bone in four individuals with SVLs between 14.4 cm to 25.0 cm. Dotted arrow: endosteal bone; black solid arrow: LAG; red solid arrow: resorption line (RL); yellow solid arrow: additional resting Line (AdL). The scale bar is equal to 200 m.
Figure 1 in Skeletochronology in long tubular bones of the Javan water monitor lizard, Varanus salvator bivittatus in the juvenile stage (Lacertilia: Varanidae)
Figure 1. Measurement of bone cross section. d: the longest part of the marrow cavity; D: the longest part of the bone diameter; MP: the widest point of bone thickness.
Figure 3 in Skeletochronology in long tubular bones of the Javan water monitor lizard, Varanus salvator bivittatus in the juvenile stage (Lacertilia: Varanidae)
Figure 3. Cross section of the seven long tubular bones of a juvenile female Varanus salvator bivittatus with one LAG (SVL: 22.2 cm). MC: marrow cavity; dotted arrow: endosteal bone; red solid arrow: LAG.
Figure 2 in Skeletochronology in long tubular bones of the Javan water monitor lizard, Varanus salvator bivittatus in the juvenile stage (Lacertilia: Varanidae)
Figure 2. Cross section of the seven long tubular bones of juvenile male Varanus salvator bivittatus with zero LAG (SVL: 14.4 cm). MC: marrow cavity; dotted arrow: endosteal bone.
Fig. 1 in The ecology, distribution, status, threats, and conservation of the Common Water Monitor (Varanus salvator) in the Dhaleswari River of Assam, India
Fig. 1. (A) Map of India, highlighting Assam. (B) Map of Assam, highlighting Hailakandi district. (C) Map of Hailakandi district showing the two rivers, Dhaleswari River and Katakhal River, with distribution of the Common Water Monitor (Varanus salvator). Dots represent sighting locations during the present survey; current distribution in the Dhaleswari River is shown in green. Further downstream, despite no present records, occurrence in the past (1970s–1980s) was reported by several interviewees (shown in yellow). No reports on present occurrence in the Katakhal River (shown in red) could be found. Map by A.S. Choudhury.
Fig. 2 in The ecology, distribution, status, threats, and conservation of the Common Water Monitor (Varanus salvator) in the Dhaleswari River of Assam, India
Fig. 2. Photographs relevant to the habitat and threats of the Common Water Monitor (Varanus salvator) in the Dhaleswari River, Assam, India. (A) Research team interacting with the locals at Rongpur 5, Hailakandi. (B) Habitat of the Common Water Monitor in the Dhaleswari River, showing bushes and other features on the banks. (C) The sandy bank of the Katakhal River, prone to erosion and landslides, is the habitat not preferred by the Common Water Monitor. (D) The sluice gate at the mouth of Dhaleswari River at Shahabad, which prevents water flow into it and diverts the water to the Katakhal River. (E) Encroachment and conversion of the Dhaleswari River into fisheries by the locals building dikes at Rongpur 2. Photos by A.S. Choudhury.
Fig. 3. A in The ecology, distribution, status, threats, and conservation of the Common Water Monitor (Varanus salvator) in the Dhaleswari River of Assam, India
Fig. 3. A Common Water Monitor (Varanus salvator) killed for venturing into a human habitation at Rongpur 6, Hailakandi. It was subsequently buried. Photo by R.A. Barbhuiya.
Using camera traps to estimate site occupancy of invasive Argentine black and white tegus (Salvator merianae) in South Florida
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Salvation Army Citadel, Sheffield
The exterior of the former Salvation Army Citadel, on the corner of Burgess Street and Cross Burgess Street, in Sheffield, U.K. This is a "listed building" (that is, protected by law from development): https://historicengland.org.uk/listing/the-list/list-entry/1247367. It has lain unused for many years. Reconstruction using Meshroom 2019.1 (and Meshlab for cleanup) from photos taken in February 2020. Source: Objaverse 1.0 / Sketchfab
How to estimate body condition in large lizards? Argentine black and white tegu (Salvator merianae, Duméril and Bibron, 1839) as a case study
<p>Body condition is a measure of the health and fitness of an organism represented by available energy stores, typically fat. Direct measurements of fat are difficult to obtain non-invasively, thus body condition is usually estimated by calculating body condition indices (BCIs) using mass and length. The utility of BCIs is contingent on the relationship of BCIs and fat, thereby validation studies should be performed to select the best-performing BCI before application in ecological investigations. We evaluated 11 BCIs in 883 Argentine black and white tegus (<em>Salvator</em> <em>merianae</em>) removed from their non-native range in South Florida, United States. Because the length-mass relationship in tegus is allometric, a segmented linear regression model was fit to the relationship between mass and length to define size classes. We evaluated percent, residual, and scaled fat and determined percent fat was the best measure of fat because it was the least associated with snout-vent length (SVL). We evaluated performance of BCIs with the full dataset and within size classes and identified Fulton's K as the best-performing BCI for our sampled population, explaining up to 19% of the variation in fat content. Overall, we found that BCIs: 1) maintained relatively weak relationships with measures of fat and 2) splitting data into size classes reduced the strength of the relationship (i.e., bias) between percent fat and SVL but did not improve the performance of BCIs. We postulate that the weak performance of BCIs in our dataset was likely due to the weak association of fat with SVL, the body plan and life-history traits of tegus, and potentially inadequate accounting of available energy resources. We caution against assuming that BCIs are strong indicators of body condition across species and suggest that validation studies be implemented, or that alternative or complementary measures of health or fitness should be considered.</p>
How to estimate body condition in large lizards? Argentine black and white tegu (Salvator merianae, Duméril and Bibron, 1839) as a case study
Open the record for dataset details and reuse information.
FIGURE 34 in Unravelling the underestimated diversity of Philippine water monitor lizards (Squamata: Varanus salvator complex), with the description of two new species and a new subspecies
FIGURE 34. Distribution ranges of the Philippine species of the V. s a l va t o r complex according to the morphological investigations presented here: V. marmoratus = red; V. nuchalis = blue; V. palawanensis sp. nov. = green; V. rasmusseni sp. nov. = black; V. c. cumingi = yellow; and V. c. s a m a re n s i s ssp. nov. = purple. Question marks denote the water monitor populations from Mindoro, Basilan, and northern Borneo of unknown taxonomic status. The grey shaded areas indicate the paleo-shorelines of several Pleistocene aggregate island complexes, which today, form biogeographic subregions of the Philippines: I = Greater Palawan; II = Greater Luzon; III = Greater Negros–Panay; IV = Greater Mindanao; and V = Greater Sulu. Map modified after Gaulke (in press).
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