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Text-fig. 5. Distribution of age classes of deningeri bears from Middle Pleistocene deposits from Za Hájovnou Cave (Moravia, the Czech Republic) based on wear stage of M2 dext. and m2 dext. (I–III: juveniles, IV–VII: prime adults, VIII–IX: senile adults; according to Stiner 1998). Juveniles distinctly outnumber adults. in Basic Population And Taphonomic Analysis Of Bear Assemblages From Za Hájovnou Cave (Moravia, The Czech Republic): A Fossil Record From 1987-2007

Text-fig. 5. Distribution of age classes of deningeri bears from Middle Pleistocene deposits from Za Hájovnou Cave (Moravia, the Czech Republic) based on wear stage of M2 dext. and m2 dext. (I–III: juveniles, IV–VII: prime adults, VIII–IX: senile adults; according to Stiner 1998). Juveniles distinctly outnumber adults.

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Text-fig. 4. Taphonomic and pathological phenomena of bear bones from Middle Pleistocene deposits from Spojovací chodba – Narozeninová chodba in Za Hájovnou Cave (Moravia, the Czech Republic). a – Mc V sin. with a pathological phenomenon on the metapodial distal part (tuberosity/exostosis?); b – gnawed juvenile ulna; c – right tibia gnawed by a large rodent (porcupine?) with detail. in Basic Population And Taphonomic Analysis Of Bear Assemblages From Za Hájovnou Cave (Moravia, The Czech Republic): A Fossil Record From 1987-2007

Text-fig. 4. Taphonomic and pathological phenomena of bear bones from Middle Pleistocene deposits from Spojovací chodba – Narozeninová chodba in Za Hájovnou Cave (Moravia, the Czech Republic). a – Mc V sin. with a pathological phenomenon on the metapodial distal part (tuberosity/exostosis?); b – gnawed juvenile ulna; c – right tibia gnawed by a large rodent (porcupine?) with detail.

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Text-fig. 3. Taphonomic and pathological phenomena of bear bones from Middle Pleistocene deposits from Chodba naděje in Za Hájovnou Cave (Moravia, the Czech Republic). a – gnawed lumbar vertebra with a bite mark on the body head; b – fragment of pelvis with a bite mark; c – femur head with a bite mark; d – Mc II dext. with a pathological phenomenon on the metapodial proximal part (tuberosity/exostosis?). in Basic Population And Taphonomic Analysis Of Bear Assemblages From Za Hájovnou Cave (Moravia, The Czech Republic): A Fossil Record From 1987-2007

Text-fig. 3. Taphonomic and pathological phenomena of bear bones from Middle Pleistocene deposits from Chodba naděje in Za Hájovnou Cave (Moravia, the Czech Republic). a – gnawed lumbar vertebra with a bite mark on the body head; b – fragment of pelvis with a bite mark; c – femur head with a bite mark; d – Mc II dext. with a pathological phenomenon on the metapodial proximal part (tuberosity/exostosis?).

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Text-fig. 9. Revultex impression of a siliceous concretion NM L 31967. A – an assemblage of three specimens of Barrandicella cf. tarda (PERNER, 1903); a – indeterminate early shell (? Barrandicella sp.), b – Mytoconula sp., ×...... B – Mytoconula sp., obligue left lateral view of an early shell just after landing on the Barrandicella surface, with a narrow flat rim of initial teleoconch shell, probably pressed down by sediment, ×......; C – the same, obligue left lateral view, ×......; D – the same, oblique right posterolateral view showing increments in the early shell, ×....... Dobrotivá F., PrahaŠárka. in Patelliconus Horný, 1961 And Mytoconula Gen. N. (Mollusca, Tergomya) From The Ordovician Of Perunica

Text-fig. 9. Revultex impression of a siliceous concretion NM L 31967. A – an assemblage of three specimens of Barrandicella cf. tarda (PERNER, 1903); a – indeterminate early shell (? Barrandicella sp.), b – Mytoconula sp., ×...... B – Mytoconula sp., obligue left lateral view of an early shell just after landing on the Barrandicella surface, with a narrow flat rim of initial teleoconch shell, probably pressed down by sediment, ×......; C – the same, obligue left lateral view, ×......; D – the same, oblique right posterolateral view showing increments in the early shell, ×....... Dobrotivá F., PrahaŠárka.

Figure 3 in Community assemblage of the Carabidae fauna in newly created habitats

Figure 3: DCA analysis of the restoration areas in comparison with the reference sites including all species (species are log transformed). The first two positions of the sample codes stand for sampling site (cf. Figure 1), the next whether the sample is from a reference site ('R') or a restoration site ('N') and the last two for the year of sampling.

Fig. 2 in Community assemblage of the Carabidae fauna in newly created habitats

Fig. 2. The number of species trapped in the restoration site Hullenzand during the first ten years after top soil removal. Species are grouped according to their habitat preference (after Turin et al., 1991).

Fig. 7 in Ground beetle assemblages (Coleoptera, Carabidae) in the third year of regeneration after a hurricane in the Puszcza Piska pine forests

Fig. 7. CCA ordination of carabid beetle assemblages inhabiting stands affected by the hurricane (P) and control stands (M) in age classes I-V. Abbreviations of the environmental variables: N – nitrogen content of soil, C – carbon content of soil, C.N – C/N ratio of soil, Dyf – soil CO 2 efflux rate. (For full names of species, see Table 1).

Fig. 4 in Ground beetle assemblages (Coleoptera, Carabidae) in the third year of regeneration after a hurricane in the Puszcza Piska pine forests

Fig. 4. Proportion of hygrophilous species individuals in carabid beetle assemblages inhabiting stands affected by the hurricane (P) and control stands (M) in age classes I-V.

Fig. 3 in Ground beetle assemblages (Coleoptera, Carabidae) in the third year of regeneration after a hurricane in the Puszcza Piska pine forests

Fig. 3. Proportion of forest species individuals in carabid beetle assemblages inhabiting stands affected by the hurricane (P) and control stands (M) in age classes I-V.

Fig. 5 in Ground beetle assemblages (Coleoptera, Carabidae) in the third year of regeneration after a hurricane in the Puszcza Piska pine forests

Fig. 5. Proportion of xerophilous species individuals in carabid beetle assemblages inhabiting stands affected by the hurricane (P) and control stands (M) in age classes I-V.

Fig. 1 in Ground beetle assemblages (Coleoptera, Carabidae) in the third year of regeneration after a hurricane in the Puszcza Piska pine forests

Fig. 1. Cluster analysis for the carabid beetle assemblages inhabiting stands affected by the hurricane (P) and control stands (M) in age classes I-V. Ward˙s method, Euclidean distance.

Fig. 6 in Ground beetle assemblages (Coleoptera, Carabidae) in the third year of regeneration after a hurricane in the Puszcza Piska pine forests

Fig. 6. The SPC/MIB (SCP/SBO) model of carabid beetle assemblages inhabiting stands affected by the hurricane (P) and control stands (M) in age classes I-V.

Fig. 4 in Assemblages of carabid beetles (Coleoptera: Carabidae) as zoo-indicator of water tourism impact on forest - lake ecotones

Fig. 4. Cluster analysis of the study sites (euclidic distances, Ward˙s method) based on carabid beetle assemblages

Fig. 1 in Assemblages of beetles (Coleoptera) in a peatbog and surrounding pine forest

Fig. 1. Comparison of species compositions of beetles registered in different habitats in the Čepkeliai Reserve in 1999 (Sorensen coefficient of similarity, UPGMA linking method).

Fig. 3 in Assemblages of carabid beetles (Coleoptera: Carabidae) as zoo-indicator of water tourism impact on forest - lake ecotones

Fig. 3. Model of state of carabid beetle assemblages in pine woodlands (B) and alder woodlands (A) in control area (0), medium pressure (1) and high pressure (2).

Fig.2 in Assemblages of carabid beetles (Coleoptera: Carabidae) as zoo-indicator of water tourism impact on forest - lake ecotones

Fig.2. Whittaker diagrams of species-abundance of carabid species in alder woodland (left side) and pine woodlands (right side).

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Figure 2 in Structure of summer bat assemblages in forests in European Russia

Figure 2. Location of main mist-netting site in the southeast part of the Voronezhsky State Nature Biosphere Reserve.

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Figure 4 in Ephemeroptera, Plecoptera, and Trichoptera assemblages of karst springs in relation to some environmental factors: a case study in central Bosnia and Herzegovina

Figure 4. CCA analyses of the EPT taxa assemblages. WT – Water temperature; pH – pH value; D – discharge; LL – leaf litter; MF – macrophytes; Cond – conductivity; SN – sand; DET – detritus.

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Figure 4 in Does the location of coastal brackish waters determine diversity and abundance of zooplankton assemblages?

Figure 4. Seasonal (monthly) changes in the total zooplankton abundance (mean, minimum, and maximum densities) (ind. dm–3) in the Vistula Lagoon and Lake Łebsko in 2010–2011.