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Fig. 5. Emys orbicularis habitat 3 in P R O J E C T S O N E M Y S O R B I C U L A R I S (R E P T I L I A: Testudines: Emydidae) In Latvia For Thirty Years (1984 - 2014): Biological Aspects, Results And Effect On Population And Ecosystems

Fig. 5. Emys orbicularis habitat 3 in Silene Nature Park before restoration (Google Earth service, SAS services).

Fig. 4. Emys orbicularis habitats 1 and 2 in P R O J E C T S O N E M Y S O R B I C U L A R I S (R E P T I L I A: Testudines: Emydidae) In Latvia For Thirty Years (1984 - 2014): Biological Aspects, Results And Effect On Population And Ecosystems

Fig. 4. Emys orbicularis habitats 1 and 2 in Silene Nature Park before (a) and after (b) restoration (Google Earth service, SAS services).

Fig. 2 in P R O J E C T S O N E M Y S O R B I C U L A R I S (R E P T I L I A: Testudines: Emydidae) In Latvia For Thirty Years (1984 - 2014): Biological Aspects, Results And Effect On Population And Ecosystems

Fig. 2. Old Emys orbicularis female, found in 1984 in Daugavpils living for 20 years in a zooculture (Photo: 2005).

Fig. 6. Emys orbicularis habitat 3 in P R O J E C T S O N E M Y S O R B I C U L A R I S (R E P T I L I A: Testudines: Emydidae) In Latvia For Thirty Years (1984 - 2014): Biological Aspects, Results And Effect On Population And Ecosystems

Fig. 6. Emys orbicularis habitat 3 in Silene Nature Park after restoration (Google Earth service, SAS services).

Fig. 7 in The biology of an isolated Mashona mole-rat population from southern Malawi, with implications for the diversity and biogeography of the genus Fukomys

Fig. 7 Violin plots showing the distribution of growth parameters (A, K, I, and maximum growth rate) calculated separately for 73 individuals of Fukomys darlingi from the Nsanje population

Fig. 6 in The biology of an isolated Mashona mole-rat population from southern Malawi, with implications for the diversity and biogeography of the genus Fukomys

Fig. 6 Growth in captive Fukomys darlingi from the Nsanje population. Mean body mass (g) calculated weekly for individuals belonging to one of four groups based on sex and breeding status (non-breeding female NB, n = 27; breeding female B, n = 13; non-breeding male NB, n = 19; breeding male B, n = 13) over a period of 10 years. Gompertz growth parameters have been estimated for each individual separately, and thereafter, mean values have been calculated for each group. These parameters have been used for modelling the solid lines

Fig. 8 in The biology of an isolated Mashona mole-rat population from southern Malawi, with implications for the diversity and biogeography of the genus Fukomys

Fig. 8 Adult body mass distribution of Fukomys darlingi from Zimbabwe (nominate form, n =18) and southern Malawi (Nsanje form, n =96). Note the larger body mass and greater sexual dimorphism in animals from Nsanje. Data on F. darlingi individuals from Goromonzi were compiled from Bennett et al. (1994), Gabathuler et al. (1996), and Herbst and Bennett (2001); animals were deemed adult when identified as breeders or when being heavier as the same-sex breeder in the respective family. Nsanje mole-rats were classified as adults at an age of 18 months

Fig. 5 in The biology of an isolated Mashona mole-rat population from southern Malawi, with implications for the diversity and biogeography of the genus Fukomys

Fig. 5 Nuclear phylogeny of Fukomys mole-rats. MCC tree estimated from nuclear datasets of five genes. Tip labels are colour-matched with those shown in the range map and the mitochondrial tree (Figs. 1 and 4). Each tip name contains the sample ID, the name of the respective CYTB lineage, and in the case of samples from F. darlingi clade also the name of the collection locality

Fig. 8 in Population structure and reproductive biology of Cichla kelberi (Perciformes, Cichlidae) in Lobo Reservoir, Brazil

Fig. 8. Monthly variation of the mean values of GSI ± Standard Deviation (SD) of Cichla kelberi females (a) and males (b), in Lobo Reservoir, during the study period.

Fig. 7 in Population structure and reproductive biology of Cichla kelberi (Perciformes, Cichlidae) in Lobo Reservoir, Brazil

Fig. 7. Histological slides of gônads of Cichla kelberi female (a – c) and male (d – f) in Lobo reservoir (Bouin, hematoxylin and eosin). a- Resting ovary with perinucleolar oocytes (100x); b- In Maturation ovary showing group synchronous development of oocytes (40x); c- Spent ovary with post-ovulatory follicles (40x); d- Resting testicle (200x); e and f- In Maturation testicle showing group synchronous development of spermatocytes (200x). Legend: O P: perinucleolar oocyte, O A: cortical alveoli oocyte, O V: vitellogenic oocyte, P F: post-ovulatory follicle, S 1: primary spermatocyte, S 2: secondary spermatocyte, S T: spermatid and S : spermatozoid.

Fig. 6 in Population structure and reproductive biology of Cichla kelberi (Perciformes, Cichlidae) in Lobo Reservoir, Brazil

Fig. 6. Monthly distribution of frequency of gonadal maturation stages of females (a) and males (b) of Cichla kelberi in the Lobo reservoir during the study. (Legend: 1- Resting; 2- In Maturation; 3- Spawning and 4- Spent).

Fig. 4 in Population structure and reproductive biology of Cichla kelberi (Perciformes, Cichlidae) in Lobo Reservoir, Brazil

Fig. 4. Distribution of the relative frequencies of occurrence of specimens of Cichla kelberi in total length classes, by seasons of the year, at Lobo Reservoir.

Fig. 5 in Population structure and reproductive biology of Cichla kelberi (Perciformes, Cichlidae) in Lobo Reservoir, Brazil

Fig. 5. Monthly variation of the mean relative condition factor values (Kn) ± Standard Deviation (SD) of Cichla kelberi females (a) and males (b), in Lobo Reservoir, during the study period. (Legend: * Kn of significantly different than 1.0).

Fig. 3 in Population structure and reproductive biology of Cichla kelberi (Perciformes, Cichlidae) in Lobo Reservoir, Brazil

Fig. 3. Distribution of the absolute frequencies of occurrence of females and males of Cichla kelberi in the total length classes – Lt - (cm) in Lobo Reservoir during the study period. (Legend: * sex ratio different than 1:1).

Fig. 2 in Population structure and reproductive biology of Cichla kelberi (Perciformes, Cichlidae) in Lobo Reservoir, Brazil

Fig. 2. Bimonthly variation of average air temperature (°C) and total rainfall (mm) at Lobo Reservoir during the first and second period of study.

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Figure 4 in Population structure and reproductive biology of the fiddler crab Uca urvillei (Brachyura: Ocypodidae) in Maputo Bay (south Mozambique)

Figure 4. Monthly percentages of ovigerous females in each month in Uca urvillei (H. Milne Edwards, 1852). The same letters above bars indicate no statistical differences among months through Scheffe's test for multiple comparisons.

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Figure 3 in Population structure and reproductive biology of the fiddler crab Uca urvillei (Brachyura: Ocypodidae) in Maputo Bay (south Mozambique)

Figure 3. Uca urvillei (H. Milne Edwards, 1852). Monthly variation of gonadosomatic index (GSI) of adult females (A) and males (B) throughout the study period. Error bars represent standard deviation.

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Figure 5 in Population structure and reproductive biology of the fiddler crab Uca urvillei (Brachyura: Ocypodidae) in Maputo Bay (south Mozambique)

Figure 5. Uca urvillei (H. Milne Edwards, 1852): ln egg number plotted against ln carapace width (mm).

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Figure 2 in Comparative population biology of Uca rapax (Smith, 1870) (Brachyura, Ocypodidae) from two subtropical mangrove habitats on the Brazilian coast

Figure 2. Uca rapax. Comparison of the median sizes of males and females at each site (A) and comparison of the median size of each sex and site (B). Boxes with at least one letter in common showed no statistically significant difference (P.0.05).