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Fig. 4 in Seasonal and spatial dispersal patterns of select ambrosia beetles (Coleoptera: Curculionidae) from forest habitats into production nurseries

Fig. 4. Mean (± SE) captures of Cnestus mutilatus, Xylosandrus compactus, X. cra`ssiusculus, and X. germanus in ethanol-baited Baker traps deployed at various distances from the nursery–forest interface at 2 sites in South Carolina in 2011 and 2012.

Fig. 3 in Seasonal and spatial dispersal patterns of select ambrosia beetles (Coleoptera: Curculionidae) from forest habitats into production nurseries

Fig. 3. Mean captures of Cnestus mutilatus, Xylosandrus compactus, X. crassiusculus, and X. germanus in ethanol-baited Baker traps at 2 sites in Louisiana and Mississippi in 2013 and 2014.

Fig. 1 in Seasonal and spatial dispersal patterns of select ambrosia beetles (Coleoptera: Curculionidae) from forest habitats into production nurseries

Fig. 1. Satellite image of the Mississippi research site (Google, Mountain View, California, USA) with an overlay showing a randomized complete block design of 5 blocks. Representing the 2013 test, each block shown here had a trap placed at −25, 25, 50, 100, and 200 m from the nursery–forest interface.

Fig. 5 in Seasonal and spatial dispersal patterns of select ambrosia beetles (Coleoptera: Curculionidae) from forest habitats into production nurseries

Fig. 5. Mean (± SE) captures of Cnestus mutilatus, Xylosandrus compactus, X. crassiusculus, and X. germanus in ethanol-baited Baker traps deployed at various distances from the nursery–forest interface at 2 sites in Louisiana and Mississippi in 2013 and 2014.

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Figure 3 in Seasonal pattern of population dynamics, spawning activities, and diet composition of sardine (Sardina pilchardus Walbaum) in the eastern Adriatic Sea

Figure 3. Alternations of the mean monthly gonadosomatic index (GSI) and values of gonad masses (Wg, g) in sardines collected by commercial purse seiners during 2013 (February–November 2013) on Croatian fishing grounds.

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Fig. 3 in Spatial and seasonal patterns in fish assemblage in Córrego Rico, upper Paraná River basin

Fig. 3. Non-metric multidimensional scaling (NMDS) ordination based on fish abundance data from Córrego Rico: a) Stretches grouped in upper, middle and lower (S1 to S7; d- dry season and r- rainy season). b) Stretches (S1 to S7; d- dry season and r- rainy season); fish species with highest correlations with the axis (Ser-het: Serrapinnus heterodon; Par-oxy: Paravandellia oxyptera; Pia-arg: Piabina argentea; Geo-bra: Geophagus brasiliensis; Ser-not: Serrapinnus notomelas; Che-est: 'Cheirodon' stenodon); environmental variables with highest correlations with the fish assemblage (Dis: discharge; Wid: width; O%: dissolved oxygen; Vel: water velocity; Am: ammonia; Nit: Nitrate). Vectors show the direction and magnitude of correlations.

Map B 1 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Map B 1. number of records per UTM 10 x 10 km square in the dataset for the analysis of the phenology.

Map B 1 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Map B 1. Number of records per UTM 10 x 10 km square in the dataset for the analysis of the habitat preferences.

Fig. 43 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 43. Principal component analysis of species according to their relative abundance in the different two-month periods.

Fig. 42 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 42. Graphical representation of the species used in the PCA-ordination according to the species main habitat. Length of the coloured parts of the stacks represent the relative number of records for each species per habitat type.

Fig. 41 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 41. Principal component analysis of species according to their relative abundance in the different main habitat types.

Fig. 20. a in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 20. a, Eluma caelata; b, Cylisticus convexus; c, Porcellio monticola; d, Porcellio scaber; e, Porcellio spinicornis; f, Porcellionides pruinosus; g, Porcellium conspersum; h, Trachelipus rathkii.

Fig. 19. a in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 19. a, Oniscus asellus; b, Philoscia affinis; c, Philoscia muscorum; d, Platyarthrus hoffmannseggii; e, Armadillidium album; f, Armadillidium nasatum; g, Armadillidium opacum; h, Armadillidium pulchellum.

Fig. 16 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 16. Corrected number of observations per two-month period for Trichoniscus provisorius (N = 157).

Fig. 29 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 29. Corrected number of observations per two-month period for Armadillidium pulchellum (N = 54).

Fig. 15 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 15. Corrected number of observations per two-month period for Trichoniscus alemannicus (N = 7).

Fig. 13 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 13. Corrected number of observations per two-month period for Trichoniscoides helveticus (N = 32).

Fig. 12 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 12. Corrected number of observations per two-month period for Trichoniscoides albidus (N = 97).

Fig. 10 in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 10. Corrected number of observations per two-month period for Metatrichoniscoides leydigii (N = 16).

Fig. 11. a in Habitat and seasonal activity patterns of the terrestrial isopods (Isopoda: Oniscidea) of Belgium

Fig. 11. a, Ligidium hypnorum; b, Androniscus dentiger; c, Haplophthalmus mengii; d, Hyloniscus riparius; e, Metatrichoniscoides leydigii; f, Trichoniscoides albidus; g, Trichoniscoides helveticus; h, Trichoniscus provisorius.