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Fig. 10 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization

Fig. 10. Trends in the relative abundance of trophic guilds in Lake Fenéki (Piscivores: y = 0.06 + 0.003x; R2 = 0.757; P> 0.00001)

Fig. 9 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization

Fig. 9. Proportion of each species in the cumulative abundance of non-native fish species in Lake Fenéki

Fig. 7 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization

Fig. 7. PCA biplot of the arcsin-square root transformed relative abundance data of the whole sampling period (1992–2011) (Variables: Sampling years; Objects: Relative abundances) (abbreviations were constructed from the Latin names of the species, using the first 3 characters of genus and species

Fig. 5 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization

Fig. 5. Estimated number of species (SD's ignored in order to improve visibility) as a function of number of individuals collected in each sampling year

Fig. 8 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization

Fig. 8. PCA biplot of the arcsin-square root transformed relative abundance data of the period 1994–2011 (Variables: Sampling years; Objects: Relative abundances)

Fig. 4 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization

Fig. 4. Relationships between the age of Lake Fenéki and the Shannon–Weaver index (y = 0.414ln(x) + 0.852; R2 = 0.772; P <0.0001)

Fig. 3 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization

Fig. 3. Relationships between the age of Lake Fenéki and the number of fish species (y = 4.141ln(x) + 3.807; R2 = 0.759; P <0.0001)

Fig. 1 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization

Fig. 1. Overlooking map of the Balaton-catchment, with the sampling site (Dark rectangle marked by the arrow indicates the flooded area of Lake Fenéki)

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Text-fig. 3. a: Panoramic reconstruction of the portion of the Govone outcrop from intervals GLA10 to GLA20 in condition of low river level. b: Transported leaf assemblage in the bottom part of bed GLA20. c: Detail of the outcrop of the leaf-bearing bed GLA20 and the underlying wood-rich layer GLA19. in Remains Of A Subtropical Humid Forest In A Messinian Evaporitebearing Succession At Govone, Northwestern Italy - Preliminary Results

Text-fig. 3. a: Panoramic reconstruction of the portion of the Govone outcrop from intervals GLA10 to GLA20 in condition of low river level. b: Transported leaf assemblage in the bottom part of bed GLA20. c: Detail of the outcrop of the leaf-bearing bed GLA20 and the underlying wood-rich layer GLA19.

Fig. 2 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization

Fig. 2. Relationships between the age of Lake Fenéki and cumulative number of specimens caught in a sampling year (y = 107.7 + 9.63x; R2 = 0.654, P = 0.001)

Figure 2 from: Kwiatkowski A (2011) Assemblages of carabid beetles (Coleoptera, Carabidae) in humid forest habitats of different stages of succession in the Puszcza Knyszyńska Forest (northeastern Poland). ZooKeys 100: 447-459. https://doi.org/10.3897/zookeys.100.1539

Figure 2 - Relationship between the contribution of forest species and the age of sampled forest stands (Spearman rank correlation coefficient rs=0.696; p=0.001)

Figure 1 from: Kwiatkowski A (2011) Assemblages of carabid beetles (Coleoptera, Carabidae) in humid forest habitats of different stages of succession in the Puszcza Knyszyńska Forest (northeastern Poland). ZooKeys 100: 447-459. https://doi.org/10.3897/zookeys.100.1539

Figure 1 - Location of the sampling plots in the Puszcza Knyszyńska forest. For specifications, see Table 1.

Figure 3 from: Kwiatkowski A (2011) Assemblages of carabid beetles (Coleoptera, Carabidae) in humid forest habitats of different stages of succession in the Puszcza Knyszyńska Forest (northeastern Poland). ZooKeys 100: 447-459. https://doi.org/10.3897/zookeys.100.1539

Figure 3 - Relationship between the contribution of large zoophages and age of the sampled forest stands (Spearman rank correlation coefficient rs=0.485; p<0.05)

Figure 4 from: Kwiatkowski A (2011) Assemblages of carabid beetles (Coleoptera, Carabidae) in humid forest habitats of different stages of succession in the Puszcza Knyszyńska Forest (northeastern Poland). ZooKeys 100: 447-459. https://doi.org/10.3897/zookeys.100.1539

Figure 4 - Multivariate analysis (RDA) carried out with the dataset (number of the sampling plots as in Table 1). See text for explanations.

Figure 4 from: Gandhi K, Epstein M, Koehle J, Purrington F (2011) A quarter of a century succession of epigaeic beetle assemblages in remnant habitats in an urbanized matrix (Coleoptera, Carabidae). ZooKeys 147: 667-689. https://doi.org/10.3897/zookeys.147.1954

Figure 4 - Dendrogram for the similarity/dissimilarity in standardized per trap catches of epigaeic beetle assemblages in sampling years 1980 and 2005 (A) and 1981 and 2005 (B) in cottonwood and oak stands, and old fields.

Figure 2 from: Gandhi K, Epstein M, Koehle J, Purrington F (2011) A quarter of a century succession of epigaeic beetle assemblages in remnant habitats in an urbanized matrix (Coleoptera, Carabidae). ZooKeys 147: 667-689. https://doi.org/10.3897/zookeys.147.1954

Figure 2 - Mean (+SE) standardized total catches of epigaeic beetles (A), and Cyclotrachelus sodalis sodalis LeConte (B) caught in 1980 and 2005 in cottonwood (N = 3) and oak (N =4) stands, and old fields (N = 2).

Figure 3 from: Gandhi K, Epstein M, Koehle J, Purrington F (2011) A quarter of a century succession of epigaeic beetle assemblages in remnant habitats in an urbanized matrix (Coleoptera, Carabidae). ZooKeys 147: 667-689. https://doi.org/10.3897/zookeys.147.1954

Figure 3 - Estimated mean species richness of epigaeic beetles using rarefaction analyses in sampling years 1980 and 2005 (A) and 1981 and 2005 (B) in cottonwood and oak stands, and old fields.

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Fig. 6 in Long-Term Development Of Fish Assemblage In Lake Fenéki (Kis-Balaton Water Protection System, Hungary): Succession, Invasion And Stabilization

Fig. 6. Relative abundance of the fish species in Lake Fenéki in the sampling years

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Figure 1 from: Gandhi K, Epstein M, Koehle J, Purrington F (2011) A quarter of a century succession of epigaeic beetle assemblages in remnant habitats in an urbanized matrix (Coleoptera, Carabidae). ZooKeys 147: 667-689. https://doi.org/10.3897/zookeys.147.1954

Figure 1 - Location of study sites in Ramsey County and major cities in Minnesota, USA.