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Figs. 2 A, B. A in Influence of the Edge Effect on A Soil Seed BAnk of A NAturAl FrAgment in the AtlAntic Forest

Figs. 2 A, B. A Linear regression of the richness and B. abundance of the soil seed bank in relation to the edge from Mata Grande of the PEI (y=Ax+B).

Fig. 5 in Application of the physical habitat simulation for fish species to assess environmental flows in an Atlantic Forest Stream in South-eastern Brazil

Fig. 5. Average habitat suitability index –HSI– in the upper and lower reach of the riacho São Pedro, for the three fish species.

Fig. 6 in Application of the physical habitat simulation for fish species to assess environmental flows in an Atlantic Forest Stream in South-eastern Brazil

Fig. 6. Weighted usable area (WUA) in the upper and lower reach of the riacho São Pedro, for the three fish species.

Fig. 4 in Application of the physical habitat simulation for fish species to assess environmental flows in an Atlantic Forest Stream in South-eastern Brazil

Fig. 4. Habitat suitability curves for depth (m), mean water column velocity (m/s) and type of substrate for the three fish species in the riacho São Pedro. Substrate types are; 1- large boulder, 2- boulder, 3- cobble, 4- gravel, 5- fine gravel, 6- sand and 7- vegetation.

Fig. 3 in Application of the physical habitat simulation for fish species to assess environmental flows in an Atlantic Forest Stream in South-eastern Brazil

Fig. 3. Frequencies of habitat availability by classes of depth (m), mean velocity (m/s) and type of substrate (1- large boulder; 2- boulder; 3- cobble; 4- gravel; 5- fine gravel; 6- sand and 7- vegetation), obtained by direct survey in the riacho São Pedro.

Fig. 1 in Application of the physical habitat simulation for fish species to assess environmental flows in an Atlantic Forest Stream in South-eastern Brazil

Fig. 1. Map of the rio Guandu basin, with indication of the studied reach in riacho São Pedro. Solid dash = small substation of CEDAE (Water and Sewer Treatment Works of Rio de Janeiro State). WTP: Water Treatment Plant.

Fig. 2 in Application of the physical habitat simulation for fish species to assess environmental flows in an Atlantic Forest Stream in South-eastern Brazil

Fig. 2. Isometric view of the cross-sections in the two target reaches of the riacho São Pedro. Grey color indicates water; solid line indicates the contour of the cross-section (in wet areas and banks).

Figure 2 in Protopolybia exigua (Hymenoptera: Vespidae) nesting on Eugenia uniflora (Myrtaceae) plant in the Atlantic Forest region

Figure 2. Protopolybia exigua (Hymenoptera: Vespidae) individual. Dorsal (A), ventral (B), lateral (C) and frontal (D) views.

Figure 1 in Protopolybia exigua (Hymenoptera: Vespidae) nesting on Eugenia uniflora (Myrtaceae) plant in the Atlantic Forest region

Figure 1. Protopolybia exigua (Hymenoptera: Vespidae) nest on a Eugenia uniflora (Myrtaceae) plant in Marechal Floriano, Espirito Santo state, Brazil. Active colony (A), external (B) and internal (C) parts of this wasp nest.

Figure 2 in Fire effects on Atlantic Forest sites from a composition, structure and functional perspective

Figure 2. Average of species richness (A), basal area (B), Shannon index (C), tree density (D), CWM Height (E), CWM Leaf length (F), CWM wood density (G), CWM Leaf deciduousness (H), CWM dispersal mode (I), CWM shade tolerance (J) for tree species inventoried in burned and unburned sites in Paraíba do Sul river basin, Southeast Atlantic Forest biome, Brazil.Same letters represent no statistical difference.

Figure 1 in Seasonality and forest edge as drivers of Tradescantia zebrina Hort. ex Bosse invasion in the Atlantic Forest

Figure 1. Mean numbers of leaves (A) and dry biomass (B) ofTradescantia zebrina in the spatial treatment (forest edge and interior) in invaded areas of the Iguaçu National Park. Error bars are standard deviation. Different letters indicate a significant difference between treatments.

Figure 1 in Anadenanthera colubrina (Fabaceae) logs in the Atlantic Forest biome: first host plant for Thoracibidion lineatocolle (Col.: Cerambycidae) and a new host for Temnopis megacephala (Col.: Cerambycidae)

Figure 1. Temnopis megacephala (A) and Thoracibidion lineatocolle (B) (Coleoptera:Cerambycidae) adults emerged from Anadenanthera colubrina (Fabaceae) logs harvested in the Atlantic Forest biome.

Fig. 3. E in Two new species of Eidmanacris (Orthoptera: Grylloidea: Phalangopsidae) from the Atlantic forest of São Paulo State, Brazil

Fig. 3. E. suassunai sp. nov. Male phallic complex: A-dorsal view; B- ventral view; C-lateral view. Female copulatory papilla: D- dorsal view; E- lateral view; F- ventral view.

Fig. 8 in Two new species of Eidmanacris (Orthoptera: Grylloidea: Phalangopsidae) from the Atlantic forest of São Paulo State, Brazil

Fig. 8. South America map with Eidmanacris species distribution (only type locality), including the new species.

Fig. 2. E in Two new species of Eidmanacris (Orthoptera: Grylloidea: Phalangopsidae) from the Atlantic forest of São Paulo State, Brazil

Fig. 2. E.suassunai sp. nov. A- male, head frontal view; B- male, head and pronotum lateral view; C- male, metanotal region; D- male, head and pronotum dorsal view; E- male supra-anal plate; F- female supra-anal plate; G- female wing; H- male, subgenital plate; I- female, subgenital plate; J- male maxillary palpi; K- ovipositor dorsal; L- ovipositor ventral; M- outer apical spurs (o. a d.- outer apical dorsal; o. a. m.- outer apical median; o. a. v.- outer apical ventral); N- inner apical spurs (i. a. d.- inner apical dorsal; i. a. m. - inner apical medium; i. a. v.- inner apical ventral); O- male femur; P- female, dorsal.

Fig. 5. E in Two new species of Eidmanacris (Orthoptera: Grylloidea: Phalangopsidae) from the Atlantic forest of São Paulo State, Brazil

Fig. 5. E. caipira sp. nov. A- male, head frontal view; B- male, head and pronotum lateral view; C- male, metanotal region; D- male, head and pronotum dorsal view; E-male supra-anal plate; F- female supra-anal plate; G- female wing; H- male, subgenital plate; I- female, subgenital plate; J- male maxillary palpi; K- ovipositor dorsal; L- ovipositor ventral; M- outer apical spurs (o. a d.- outer apical dorsal; o. a. m.- outer apical median; o. a. v.- outer apical ventral); N- inner apical spurs (i. a.d.- inner apical dorsal; i. a. m. - inner apical medium; i. a. v.- inner apical ventral); O- male femur; P- female, dorsal.

Fig. 6. E in Two new species of Eidmanacris (Orthoptera: Grylloidea: Phalangopsidae) from the Atlantic forest of São Paulo State, Brazil

Fig. 6. E. caipira sp. nov. Male phallic complex: A-dorsal view; B- ventral view; C-lateral view. Female copulatory papilla: D- dorsal view; E- lateral view; F- ventral view.

Fig. 3 in Avian Assemblages in Forest Fragments do not Sum to the Expected Regional Community in the Brazilian Atlantic Forest.

Fig. 3. The number of local Atlantic Forest species by forest fragment size (log10 scales), showing that the number increases with fragment size (F = 13.4, r2 = 0.625, p = 0.0065).

Fig. 2 in Avian Assemblages in Forest Fragments do not Sum to the Expected Regional Community in the Brazilian Atlantic Forest.

Fig. 2. Numbers of species and similarities (PCoA) among the 10 Atlantic Forest fragments in southern Bahia, Brazil. A) Species accumulation curves, illustrating that with over 5000 sightings, the predicted total number of species had not been reached in any fragment, or in all fragments combined. Also, the similarity of the curves and their lack of a relationship with fragment size suggests that all fragments are similar with respect to accumulation of species. Note that both axes are log10 scaled. B) Principal Coordinate Analysis, using Bray similarities, illustrating that similarity among fragments was always low. Larger symbols indicate fragment centroids, and each smaller point indicates a sample list of species (see text). No particular pattern is evident, and all fragments are variable and do not form groups based on fragment size.

Fig. 4 in Avian Assemblages in Forest Fragments do not Sum to the Expected Regional Community in the Brazilian Atlantic Forest.

Fig. 4. Functional diversity analysis comparing different-sized fragments and functional evenness, dispersion, and divergence. A–C: Black squares and lines indicate the Atlantic Forest expected regional assemblage, circles and lines indicate the observed assemblages, with blue indicated only the Atlantic Forest species, and the open circle indicates all observed species (all based on presence-absence). D–F: estimated from presence-absence data of the expected local assemblage that were absent from the fragment. Regression results are presented in table 3.