O propósito deste estudo foi investigar os efeitos da estrutura do sub-bosque na comunidade de colêmbolos. Foram comparados quatro ambientes florestais distintos: plantações de Pinus spp., plantações de Eucalyptus spp., plantações de Araucaria angustifolia e áreas de floresta ombrófila nativa remanescente. Para cada fisionomia vegetal houve três áreas com duas unidades amostrais de 25 m × 2 m cada. As coletas foram realizadas com guarda-chuva entomológico, medindo 1 m × 1 m, no período de setembro de 2003 a agosto de 2004. Investigou-se se a abundância, a riqueza e a diversidade da comunidade de colêmbolos foram influenciadas pelas fisionomias vegetais. Também verificou-se se a estrutura do habitat de cada tipo de floresta teve associação com a composição da comunidade de colêmbolos. Foram coletados 4111 indivíduos, pertencentes às famílias Entomobryidae, Tomoceridae e Sminthuridae, divididos em 12 morfoespécies. A plantação de Pinus spp. apresentou maior riqueza, abundância e diversidade de colêmbolos, devido à maior quantidade de vegetação disponível no sub-bosque. A composição de colêmbolos esteve associada aos tipos vegetacionais, com Entomobryidae e Sminthuridae associados aos arbustos, e Tomoceridade às árvores. A estrutura do habitat, medida através da densidade e composição da vegetação do sub-bosque mostrou-se um fator importante na determinação da estrutura e composição da comunidade de Collembola.

The purpose of this study was to investigate the effects of different landscape structures on the understory Collembola community. Four different forest physiognomies were compared: Pinus spp. plantation, Eucalyptus spp. plantation, Araucaria angustifolia plantation, and a remaining native Araucaria forest. Three areas containing two sampling units (25 m x 2 m each) were selected in each forest physiognomy. Understory Collembola collection was done with a 1 x 1m canvas sheet held horizontally below the vegetation, which was beaten with a 1m long stick, seasonally from September 2003 to August 2004. We evaluated the influence of forest physiognomies on the abundance, richness and diversity of Collembola communities. It was also verified if the habitat structure of each physiognomy was associated with the composition of the Collembola community. A total number of 4,111 individuals were collected belonging to the families Entomobrydae and Tomocerida (Entomobryomorpha), and Sminthuridae (Symphypleona), and divided in 12 morphospecies. Pinus plantation presented the highest richness, abundance and diversity of Collembola and it was associated to diverse understory vegetation. The abundance of Entomobrydae and Sminthuridae was associated to the presence of bushes, while Tomoceridae abundance was associated to the presence of trees. The habitat structure, measured through understory vegetation density and composition, plays an important role on the determination of the structure and composition of the Collembola community.

A survey of carnivore mammals was accomplished in Aparados da Serra National Park from February 1998 to March 2000. The park has 10,250 ha and is considered a biodiversity core area of the Atlantic Forest Biosphere Reserve in the Rio Grande do Sul State, Brazil. The landscape is characterized by relatively well preserved relicts of Araucaria angustifolia (Bertol.) Kuntze forest, grasslands and Atlantic Forest, which have contributed for the survival of endangered carnivore mammals. The National Park was divided in a grid of 16 km² cells using a 1:50,000 scale map. The animals were recorded using indirect methods, by identifying signs (scats, tracks) and direct observation in 2.5 km long and 5 m wide transects, with 10 replicates in each grid cell. Interviews with local people were also used to confirm the animal presence. A total of 13 species was recorded: Procyon cancrivorus (Cuvier, 1798), Pseudalopex gymnocercus (G. Fischer, 1814), Leopardus pardalis (Linnaeus, 1758) and Cerdocyon thous (Linnaeus, 1766) were the most frequent species registered. Nasua nasua (Linnaeus 1766), Herpailurus yaguarondi (Lacépède, 1809), Chrysocyon brachyurus (Illiger, 1815), Eira barbara (Linnaeus, 1758), Leopardus sp., Puma concolor (Linnaeus, 1771), Galictis cuja (Molina, 1782), Conepatus chinga (Molina, 1892) and Lontra longicaudis (Olfers, 1818) showed lower frequencies. The Park presented areas with significant differences (Mantel Test, P< 0.05) in species richness and composition related to habitat classes. Areas with high habitat richness presented high species richness. The Araucaria forest was the habitat that presented the higher carnivore richness. The border areas of the Park are influenced by several environmental degradation factors that could be affecting the distribution of carnivores.