A vegetação da Ilha Grande faz parte do Bioma Floresta Atlântica, que possui altos índices de biodiversidade e cobre amplas regiões de zonas climáticas e formações vegetacionais tropicais a subtropicais. No Brasil, estende-se numa estreita faixa ao longo de quase toda a costa atlântica e interioriza-se atingindo parte da Argentina e do Paraguai. Asteraceae é a terceira maior família em número de espécies na Floresta Atlântica. Assim, buscou-se conhecer a representatividade dessa família na Ilha Grande, objetivando contribuir com a política de preservação e manutenção de seus ecossistemas. Nesse contexto, promoveu-se um levantamento bibliográfico, consultas a herbários e excursões periódicas de coleta em campo. O material coletado foi depositado no herbário da Universidade do Estado do Rio de Janeiro (HRJ). Registrou-se na área de estudo 67 espécies subordinadas a 37 gêneros. Os gêneros são a seguir denominados: Achyrocline (3 spp.), Adenostemma (1sp.), Ageratum (1 sp.), Austrocritonia (1 sp.), Astroeupatorium (1 sp.), Baccharis (8 spp.), Bidens (1 sp.), Blainvillea (1 sp.), Centratherum (1 sp.), Chaptalia (1 sp.), Chromolaena (3 spp.), Conyza (1 sp.), Cosmos (1 sp.), Eclipta (1 sp.), Elephantopus (2 spp.), Emilia (1 sp.), Erechtites (1 sp.), Galinsoga (1 sp.), Gamochaeta (1 sp.), Grazielia (1 sp.), Heterocondylus (2 spp.), Mikania (13 spp.), Piptocarpha (2 spp.), Pluchea (1 sp.), Praxelis (1 sp.), Pseudogynoxys (1 sp.), Pterocaulon (1 sp.), Sphagneticola (1 sp.), Sonchus (1 sp.), Steymarkina (1 sp.), Struchium (1 sp.), Synedrella (1 sp.), Tilesia (1 sp.), Tithonia (1 sp.), Trixis (1 sp.), Verbesina (1 sp.) e Vernonia (5 spp.). Estes gêneros estão abrigados sob nove tribos. São citadas pela primeira vez para o Estado do Rio de Janeiro as espécies Mikania campanulata e Struchium sparganophorum. / The vegetation of Ilha Grande is part of the Atlantic forest biome, which has a high rainfall index and extends over wide climatic regions and tropical and subtropical plant formations. In Brazil, it spreads on a narrow strip along all of the atlantic coast and moves inland as far as Argentina and Paraguay. Asteraceae is the third major Family in Atlantic forest species. Hence, one has tried to know the representativeness of that family in Ilha Grande, aiming at contributing to the preservation and maintenance of their ecosystems. In this context, one has made a bibliographic survey, consultations to herbariums and periodic field trips for data colllection. The collected material has been taken to the herbarium of Rio de Janeiro State University (UERJ) (HRJ). 67 species subordinated to 37 genera have been registered in the area, The genera are denominated as follows: Achyrocline (3 spp.), Adenostemma (1sp.), Ageratum (1 sp.), Austrocritonia (1 sp.), Astroeupatorium (1 sp.), Baccharis (8 spp.), Bidens (1 sp.), Blainvillea (1 sp.), Centratherum (1 sp.), Chaptalia (1 sp.), Chromolaena (3 spp.), Conyza (1 sp.), Cosmos (1 sp.), Eclipta (1 sp.), Elephantopus (2 spp.), Emilia (1 sp.), Erechtites (1 sp.), Galinsoga (1 sp.), Gamochaeta (1 sp.), Grazielia (1 sp.), Heterocondylus (2 spp.), Mikania (13 spp.), Piptocarpha (2 spp.), Pluchea (1 sp.), Praxelis (1 sp.), Pseudogynoxys (1 sp.), Pterocaulon (1 sp.), Sphagneticola (1 sp.), Sonchus asper (1 sp.), Steymarkina (1 sp.) Struchium (1 sp.), Synedrella (1 sp.), Tilesia (1 sp.), Tithonia (1 sp.), Trixis (1 sp.), Verbesina (1 sp.) e Vernonia (5 spp.). These genera are located in nine tribes. The following species are cited to Rio de Janeiro State for the first time: Mikania campanulata e Struchium sparganophorum.

A vegetação da Ilha Grande faz parte do Bioma Floresta Atlântica, que possui altos índices de biodiversidade e cobre amplas regiões de zonas climáticas e formações vegetacionais tropicais a subtropicais. No Brasil, estende-se numa estreita faixa ao longo de quase toda a costa atlântica e interioriza-se atingindo parte da Argentina e do Paraguai. Asteraceae é a terceira maior família em número de espécies na Floresta Atlântica. Assim, buscou-se conhecer a representatividade dessa família na Ilha Grande, objetivando contribuir com a política de preservação e manutenção de seus ecossistemas. Nesse contexto, promoveu-se um levantamento bibliográfico, consultas a herbários e excursões periódicas de coleta em campo. O material coletado foi depositado no herbário da Universidade do Estado do Rio de Janeiro (HRJ). Registrou-se na área de estudo 67 espécies subordinadas a 37 gêneros. Os gêneros são a seguir denominados: Achyrocline (3 spp.), Adenostemma (1sp.), Ageratum (1 sp.), Austrocritonia (1 sp.), Astroeupatorium (1 sp.), Baccharis (8 spp.), Bidens (1 sp.), Blainvillea (1 sp.), Centratherum (1 sp.), Chaptalia (1 sp.), Chromolaena (3 spp.), Conyza (1 sp.), Cosmos (1 sp.), Eclipta (1 sp.), Elephantopus (2 spp.), Emilia (1 sp.), Erechtites (1 sp.), Galinsoga (1 sp.), Gamochaeta (1 sp.), Grazielia (1 sp.), Heterocondylus (2 spp.), Mikania (13 spp.), Piptocarpha (2 spp.), Pluchea (1 sp.), Praxelis (1 sp.), Pseudogynoxys (1 sp.), Pterocaulon (1 sp.), Sphagneticola (1 sp.), Sonchus (1 sp.), Steymarkina (1 sp.), Struchium (1 sp.), Synedrella (1 sp.), Tilesia (1 sp.), Tithonia (1 sp.), Trixis (1 sp.), Verbesina (1 sp.) e Vernonia (5 spp.). Estes gêneros estão abrigados sob nove tribos. São citadas pela primeira vez para o Estado do Rio de Janeiro as espécies Mikania campanulata e Struchium sparganophorum. / The vegetation of Ilha Grande is part of the Atlantic forest biome, which has a high rainfall index and extends over wide climatic regions and tropical and subtropical plant formations. In Brazil, it spreads on a narrow strip along all of the atlantic coast and moves inland as far as Argentina and Paraguay. Asteraceae is the third major Family in Atlantic forest species. Hence, one has tried to know the representativeness of that family in Ilha Grande, aiming at contributing to the preservation and maintenance of their ecosystems. In this context, one has made a bibliographic survey, consultations to herbariums and periodic field trips for data colllection. The collected material has been taken to the herbarium of Rio de Janeiro State University (UERJ) (HRJ). 67 species subordinated to 37 genera have been registered in the area, The genera are denominated as follows: Achyrocline (3 spp.), Adenostemma (1sp.), Ageratum (1 sp.), Austrocritonia (1 sp.), Astroeupatorium (1 sp.), Baccharis (8 spp.), Bidens (1 sp.), Blainvillea (1 sp.), Centratherum (1 sp.), Chaptalia (1 sp.), Chromolaena (3 spp.), Conyza (1 sp.), Cosmos (1 sp.), Eclipta (1 sp.), Elephantopus (2 spp.), Emilia (1 sp.), Erechtites (1 sp.), Galinsoga (1 sp.), Gamochaeta (1 sp.), Grazielia (1 sp.), Heterocondylus (2 spp.), Mikania (13 spp.), Piptocarpha (2 spp.), Pluchea (1 sp.), Praxelis (1 sp.), Pseudogynoxys (1 sp.), Pterocaulon (1 sp.), Sphagneticola (1 sp.), Sonchus asper (1 sp.), Steymarkina (1 sp.) Struchium (1 sp.), Synedrella (1 sp.), Tilesia (1 sp.), Tithonia (1 sp.), Trixis (1 sp.), Verbesina (1 sp.) e Vernonia (5 spp.). These genera are located in nine tribes. The following species are cited to Rio de Janeiro State for the first time: Mikania campanulata e Struchium sparganophorum.

This study examines the effects of clearcut regeneration with whole-tree harvesting on plant diversity. Three approaches were used to study changes in species composition and structure: (1) forest level, (2) stand level, and (3) diversity indices. Within each approach the forest was stratified into three horizontal vegetative regions based upon height: herb (< 1 m), shrub (between 1 and 5 m), and tree (> 5 m). Between the pre-harvest and 17-year-old forest, the relative percent cover of 3 out of 45 herbaceous and 2 out of 34 woody species were found to be significantly different (df = 3; a = 0.10) in the herb stratum; the importance value (average of relative basal area and stem density) of 2 out of 25 woody species in the shrub stratum; and 1 out of 21 woody species in the tree stratum. Within stands, the three lower quality, 17-year-old stands (SI50 = 12.2, 15.2, and 18.3 m) most resembled their pre-harvest composition; however, increases in ericaceous species were observed in the herb and shrub strata potentially inhibit the future regeneration of tree species. The SI50 = 21.3 m stand incurred the greatest changes in composition potentially due to the lack of fire as a disturbance mechanism. The major mechanism that has caused the shifts in species composition and structure is the change in the microenvironment due to the removal of the overstory, which has shifted the competitive advantages from one species to another. In all cases, diversity indices were not found to be significantly different between the 17-year-old and pre-harvest forests. Diversity indices were therefore determined to have limited use if a manager wants to know specific compositions and/or abundance of species. / Master of Science

Increasing evidence documenting the decline of insect populations, resulting from increasing human disturbances has resulted in efforts to establish pollinator gardens to provide additional resources for insect populations. However, our understanding of biotic and abiotic garden characteristics important for attracting and sustaining pollinator diversity is limited. Here, we evaluated 17 pollinator gardens to evaluate the effect of five biotic and three abiotic garden characteristics on pollinator species richness, abundance, and proportional representation of four pollinator functional groups. Plant species richness positively influenced pollinator richness and negatively influenced flower visitation. Bombus proportional abundance responded to several variables (distance to vegetation, plant species richness, floral symmetry, floral native status, habitat type), and decreases in their proportional representation were accompanied by increasing proportions of other insect groups. Our results suggest any size, diverse, native pollinator gardens can improve pollinator diversity, and small-scale pollinator gardens should favor functional groups adapted for the habitat type.