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Fig. 1 in Effect of vegetation and abiotic factors on the abundance and population structure of Crocodylus acutus (Cuvier, 1806) in coastal lagoons of Colima, Mexico

Fig. 1. Selected sites in the study area. Acronym definitions and characteristics of the sites are given in Table 1.

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Fig. 2 in Effect of vegetation and abiotic factors on the abundance and population structure of Crocodylus acutus (Cuvier, 1806) in coastal lagoons of Colima, Mexico

Fig. 2. Non-metric Multidimensional Scaling (NMDS) analysis showing the formation of two groups, by taking into account the crocodiles observed, water salinity, temperature, depth, and the four vegetation types present. Acronym definitions and characteristics of the sites are given in Table 1.

Fig. 6 in Diversity and spatial distribution of predacious Dolichopodidae (Insecta: Diptera) on organic vegetable fields and adjacent habitats in Brazil

Fig. 6. Grouping of assemblies Dolichopodidae flies in different habitats: vegetables, fallow, agroforestry, and native vegetation based on coefficient similarity (Bray-Curtis) on organic farms cultivating vegetables in the Federal District, Brazil.

Fig. 5 in Diversity and spatial distribution of predacious Dolichopodidae (Insecta: Diptera) on organic vegetable fields and adjacent habitats in Brazil

Fig. 5. Number of exclusive and shared (intersections) Dolichopodidae species in vegetable crops and fallow habitats, agroforestry, and native vegetation.

Fig. 2 in Diversity and spatial distribution of predacious Dolichopodidae (Insecta: Diptera) on organic vegetable fields and adjacent habitats in Brazil

Fig. 2. Mean abundance (± SE) of Dolichopodidae flies collected in different rural properties with vegetable crops, fallow, agroforestry, and native vegetation in the Federal District, Brazil.

Fig. 1 in Diversity and spatial distribution of predacious Dolichopodidae (Insecta: Diptera) on organic vegetable fields and adjacent habitats in Brazil

Fig. 1. Organic vegetable farms sampled in Ceilândia (I), Taguatinga (II), Paranoá (III), and Lamarão (IV), Federal District, Brazil.

Fig. 4 in Diversity and spatial distribution of predacious Dolichopodidae (Insecta: Diptera) on organic vegetable fields and adjacent habitats in Brazil

Fig. 4. Adjustment to the log normal distribution model of the Dolichopodidae assembly per habitat on organic farms producing vegetable in the Federal District, Brazil.

Fig. 3 in Diversity and spatial distribution of predacious Dolichopodidae (Insecta: Diptera) on organic vegetable fields and adjacent habitats in Brazil

Fig. 3. Distribution of relative abundance by species of Dolichopodidae flies collected on organic farms producing vegetables in the Federal District, Brazil.

Fig. 2 in Impact of years in bahiagrass and cultivation techniques in organic vegetable production on epigeal arthropod populations

Fig. 2. Mean abundance of total predatory beetles during the 4 crop rotation in 2013. An asterisk (*) denotes significant effects (P <0.05) of yr in bahiagrass. Double asterisks (**) denote significant effects of tillage method.

Fig. 1 in Impact of years in bahiagrass and cultivation techniques in organic vegetable production on epigeal arthropod populations

Fig. 1. Mean abundance of total carabid beetles during the 4 crop rotation in 2013. An asterisk (*) denotes significant effects (P <0.05) of yr in bahiagrass. Double asterisks (**) denote significant effects of tillage method.

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Fig. 1. Location and vegetation types where small mammals were sampled between November 2012 and September 2013 in Small mammals from the lasting fragments of Araucaria Forest in southern Brazil: a study about richness and diversity

Fig. 1. Location and vegetation types where small mammals were sampled between November 2012 and September 2013, at Piraí do Sul National Forest, ParanÁ state, Brazil (A, Pine Plantation; B, Riparian Forest; C, Araucaria Plantation; D, Natural Regeneration forest; E, High Altitude forest). Original distribution of Atlantic Forest biome (light gray) and Araucaria forest (dark gray).

Fig. 4 in Assessment of the predatory capacity on mosquito larvae of Jenynsia multidentata (Anablepidae) in presence of vegetation under laboratory conditions

Fig. 4. Daily consumption (mean ±SD) of Jenynsia multidentata (Jenyns, 1842) on 120 Culex pipiens Linnaeus, 1758 fourth-stage larvae. (T1) 20 stems, (TC) without stems, for 5 days.

Fig. 2 in Assessment of the predatory capacity on mosquito larvae of Jenynsia multidentata (Anablepidae) in presence of vegetation under laboratory conditions

Fig. 2. Daily consumption (mean ±SD) of Jenynsia multidentata (Jenyns, 1842) on 60 Culex pipiens Linnaeus, 1758 fourth-stage larvae at different densities of vegetation: (T1) 20 stems, (T2) 10 stems and (TC) without stems, for 5 days.

Fig. 1 in Assessment of the predatory capacity on mosquito larvae of Jenynsia multidentata (Anablepidae) in presence of vegetation under laboratory conditions

Fig. 1. Jenynsia multidentata (Jenyns, 1842) consumption of 60 Culex pipiens Linnaeus, 1758 fourth-stage larvae at different vegetation densities: (T1) 20 stems, (T2) 10 stems and (TC) without stems. Each circle represents the daily consumption of a female specimen and the horizontal bars indicate the average consumption. The letters (a, b) at the top of the figure indicate significant differences between treatments (p <0.05).

Fig. 3 in Assessment of the predatory capacity on mosquito larvae of Jenynsia multidentata (Anablepidae) in presence of vegetation under laboratory conditions

Fig. 3. Jenynsia multidentata (Jenyns, 1842) consumption of 120 Culex pipiens Linnaeus, 1758 fourth-stage larvae at different vegetation densities: (T1) 20 stems and (TC) without stems. Each circle represents the daily consumption of a female specimen and the horizontal bars indicate the average consumption.

Figure S4 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure S4. Unweighted Pair Group Method with Arithmetic Mean (UPGMA) based on Gower distance measure indicating annual forb plant functional types (PFTs).

Figure S5 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure S5. Unweighted Pair Group Method with Arithmetic Mean (UPGMA) based on Gower distance measure indicating perennial forb plant functional types (PFTs).

Figure S3 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure S3. Unweighted Pair Group Method with Arithmetic Mean (UPGMA) based on Gower distance measure indicating perennial grass plant functional types (PFTs).

Figure S1 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure S1. Principal Co-ordinate Analysis (PCoA) scatter diagram of the species-trait matrix revealing a strong clustering based on life history.

Figure 3 in Effects of land-use change on herbaceous vegetation in a semi-arid Mopaneveld savanna

Figure 3. Herbaceous species (left) and trait (right) diversity measures benchmarked against the mean value calculated for the untransformed (protected) area (----) across transformed land-use types. Vertical bars denote 0.95 confidence intervals. Significant deviations from the protected area (Sidak posthoc pairwise comparison; p<0.05) are denoted by (*).