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Fig. 1. The potential distribution map for B in Long-Term Bioclimatic Modelling The Distribution Of The Fire-Bellied Toad, Bombina Bombina (Anura, Bombinatoridae), Under The Influence Of Global Climate Change

Fig. 1. The potential distribution map for B. bombina under contemporary climatic conditions. The colour gradient represents high (red) to low (green) habitat suitability for the species.

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Fig. 4. The potential distribution map for B. bombina under projected 2050 in Long-Term Bioclimatic Modelling The Distribution Of The Fire-Bellied Toad, Bombina Bombina (Anura, Bombinatoridae), Under The Influence Of Global Climate Change

Fig. 4. The potential distribution map for B. bombina under projected 2050 climatic conditions. The colour gradient represents high (red) to low (green) habitat suitability for the species.

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Fig 3 in Long-Term Bioclimatic Modelling The Distribution Of The Fire-Bellied Toad, Bombina Bombina (Anura, Bombinatoridae), Under The Influence Of Global Climate Change

Fig 3. Response curve showing how the logistic prediction changes as the environmental variable Bio2 (Mean diurnal temperature range, oC, X-axis) is varied, keeping all other environmental variables at their average sample value. The curve shows the mean response of the 10 replicate Maxent runs (red) and and the mean +/– one standard deviation (blue).

Figure 1 in Two cases of unclear hindlimb malformation in Bombina variegata

Figure 1. Observed individuals of Bombina variegata with a hind limb malformations from Shëndelli Mts., Albania: (A) ventral view, (B) dorsal view; and Lacul Poiana Mărului, Romania: (C) ventral view, (D) dorsal view.

Fig. 7 in Reciprocal Predation Between Preserved And Invasive Species: Adult Bombina Bombina Predate Young Whitebaits Of Alien Fish Perccottus Glenii

Fig. 7. Dynamics of relative predation (% from existed number of live whitebaits) for all model populations of B. bombina.

Fig. 1 in Reciprocal Predation Between Preserved And Invasive Species: Adult Bombina Bombina Predate Young Whitebaits Of Alien Fish Perccottus Glenii

Fig. 1. Overlapping areas of B. bombina and P. glenii distribution in Latvia (Pupina et al. In press).

Fig. 9 in Reciprocal Predation Between Preserved And Invasive Species: Adult Bombina Bombina Predate Young Whitebaits Of Alien Fish Perccottus Glenii

Fig. 9. Scheme of the reciprocal predation between B. bombina and its invasive threat P. glenii registered in the study.

Fig. 5 in Reciprocal Predation Between Preserved And Invasive Species: Adult Bombina Bombina Predate Young Whitebaits Of Alien Fish Perccottus Glenii

Fig. 5. Number of left live, predated, and died/ killed P. glenii in all experimental groups in total after the experiment.

Fig. 3 in Reciprocal Predation Between Preserved And Invasive Species: Adult Bombina Bombina Predate Young Whitebaits Of Alien Fish Perccottus Glenii

Fig. 3. Dynamics of number of live, predated, and died/killed P. glenii in different B. bombina model populations (Bb-1, Bb-2, Bb-3, and Bb-4).

Fig. 2 in Macro-Scale Environmental Preferences Of Bombina Bombina: A Modeling Approach

Fig. 2. The receiver operating characteristic (ROC) curve generated in Maxent, showing an average of 50 repetitions of the model; the dark blue range shows the mean of the standard deviations.

Fig. 8 in Action Plan For The Fire-Bellied Toad Bombina Bombina In Latvia: Assessment Of The Implementation For Ten Years, Releasing From Aquaculture And Restoration Of Habitats In 2006-2016

Fig. 8. Fitted linear model of the relationship between Actions' implementation before and after BAP.

Fig. 7 in Action Plan For The Fire-Bellied Toad Bombina Bombina In Latvia: Assessment Of The Implementation For Ten Years, Releasing From Aquaculture And Restoration Of Habitats In 2006-2016

Fig. 7. Box-and-Whicker plots for Species Conservation and Habitats Conservation Sub-actions' implementation in points before and after BAP.

Fig. 3 in Macro-Scale Environmental Preferences Of Bombina Bombina: A Modeling Approach

Fig. 3. Results of jackknife test of variable importance, using training gain. The jackknife test in blue bars shows individual environmental variable importance relative to the red bar which shows all environmental variables. Light blue bar shows whether a variable has any information that isn't present in the other variables, and a dark blue bar shows whether a variable has any useful information by itself. Values shown are averages over replicate runs.

Fig.2 in Fenetic Analysis Of Bombina Bombina Ventral Spots Pattern In 8 Localizations In Latvia

Fig.2. The frequency of ventral phenomorphs (1-15) occurrences in Bombina bombina samplings (n=72) from different localizations in Latvia

Fig.8 in Fenetic Analysis Of Bombina Bombina Ventral Spots Pattern In 8 Localizations In Latvia

Fig.8. The ratio of different clusters of ventral Received: 30.04.2008. phenomorphs occurrence in the examined Accepted: 01.06.2009. Bombina bombina samplings (n=72).

Fig.5 in Fenetic Analysis Of Bombina Bombina Ventral Spots Pattern In 8 Localizations In Latvia

Fig.5. The ratio of registered clusters of ventral phenomorphs in Bombina bombina samplings (n=72) from different localizations (n=8). (Latvia) for the consultations and cooperation.

Fig.4 in Fenetic Analysis Of Bombina Bombina Ventral Spots Pattern In 8 Localizations In Latvia

Fig.4. The frequency of ventral phenomorphs' clusters occurrence in Bombina bombina samplings (n=72) from different localizations.

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Figure 3 in First record of Bombina variegata (L., 1758) (Anura: Bombinatoridae) from Turkey

Figure 3. General views of the toads in their natural habitat. (a- Dorsal view of a female specimen; b- Ventral view of a female specimen; c- Dorsal view of a male specimen; d- Ventral view of a male specimen; e- The toads swimming in their breeding pond; f- Unken reflex of a male specimen).