O presente trabalho teve como objetivo investigar a resiliência de uma área desflorestada há aproximadamente 20 anos, ocupada atualmente com pastagem e cultivo de Citrus sp. Essa resiliência foi avaliada através dos seguintes aspectos da dinâmica florestal: análise do banco de sementes, da chuva de sementes e de indivíduos jovens regenerantes. Este trabalho foi conduzido no Parque Estadual do Jurupará (23°51' S e 47°11' W), abrangendo os municípios paulistas de Ibiúna e Piedade, em uma região de transição entre a Floresta Ombrófila Densa e a Floresta Estacional Semidecidual. Foram alocadas três faixas de amostragem, cada uma com cinco parcelas aleatorizadas de 10 X 20 m, uma num trecho ocupado com um plantio abandonado de Citrus sp, adjacente ao remanescente florestal, e as restantes num trecho ocupado com pastagem, uma a 0-20 m e outra a 80-100 m de distância do remanescente florestal. Para a avaliação da chuva de sementes, foram lançados aleatoriamente em cada parcela três coletores de sementes circulares de 0,52 m de diâmetro, com coletas mensais das sementes depositadas. Para a avaliação do banco de sementes foram instalados em cada parcela, três subparcelas de 0,25 X 0,25 m, para coleta de solo até 0,05 m de profundidade em duas épocas distintas: estação chuvosa (janeiro/2001) e na estação seca (agosto/2001). Para a avaliação dos indivíduos jovens regenerantes, foram implantadas aleatoriamente 4 subparcelas de 0,5 X 0,5 m, nas quais foram realizadas três avaliações de todos os indivíduos arbustivos-arbóreos com altura entre 0,30 e 1,30 m. Na avaliação da chuva de sementes na área ocupada com o cultivo de Citrus sp, foi observada alta densidade de sementes autóctones de espécies arbustivo-arbóreas (Leandra sp. com 20.638,73 sem.m -2 e Tibouchina sp. com 12.681,85 sem.m -2 ) que ocupavam a área junto com aos indivíduos de Citrus sp. Na pastagem verificou-se a predominância de espécies ruderais, a densidade média das espécies arbustivo-arbóreas foi de 335,75 sem.m -2 , na pastagem próxima do remanescente florestal e de 577,58 sem.m -2 na pastagem distante do remanescente florestal. Na avaliação do banco de sementes no cultivo de Citrus sp, as espécies ruderais consistiram em 99,88% das espécies germinadas na estação chuvosa, e 99,73% na estação seca. Na pastagem, na estação chuvosa, para as duas distâncias, 100% das espécies germinadas eram espécies herbáceas tipicamente ruderais; na estação seca esta forma de vida predominou em 99,66% na área próxima ao remanescente florestal e 99,92% na área mais distante. No levantamento dos indivíduos jovens regenerantes, encontrou-se densidade 5,8 ind.m -2 na área de Citrus sp e de 1,2 ind.m -2 e 2,2 ind.m -2 na pastagem a 0-20 m e 80-100 m de distância do remanescente florestal, respectivamente. Apenas na chuva de sementes foram encontradas diferenças significativas entre a área de Citrus sp e a pastagem, para os demais aspectos analisados não foram encontradas diferenças significativas entre a área de Citrus sp e pastagem. Na pastagem, para todos os apectos analisados, não foram encontradas diferenças significativas entre as diferentes distâncias, rejeitando a hipótese de que a resiliência da pastagem estudada está inversamente relacionada com as distâncias do remanescente florestal nesse trabalho. / This work had as a goal identifying the resilience of an area, which was deforested in the past, currently used as pasture and Citrus sp crop. This resilience was evaluated through the following aspects of forest dynamics: soil seed bank analysis, seed rain and saplings. It was conducted in the Jurupará State Park in Ibiúna and Piedade (São Paulo State), in a transition area between the Ombrophil Forest and the Semideciduous Seasonal Forest. In this area, three sampling strips were allocated, each one with five 10 X 20 m plots, being one inside the Citrus sp crop and the others inside the pasture, distant 0-20 m and 80-100 m from the forest remant. For evaluating the seed rain, three circular seeds collectors of 0.52 cm in diameter were randomly set in each plot, with monthly samplings of the deposited seeds. For evaluating the seed bank, soil of three 0.25 X 0.25 m sub-plots and 0.05 m deep was collected in two different seasons: rainy season (January/2001) and dry season (August/2001). To the saplings evaluation, four 0.5 X 0.5 m sub-plots were implanted randomly, in which three evaluations of all the shrubs and trees individuals (0.30-1.30m height) were performed. At the seed rain inside the Citrus sp crop, a high density of autoctone seed of shrubs and trees species (Leandra sp. with 20,638.73 seed.m -2 and Tibouchina sp. with 12,681.85 seeds.m -2 ) was observed; inside the pasture, there were a predominance of ruderal species, while the average density of shrubs and trees species were, 335.75 seeds.m -2 in the pasture distant 0-20m from the remaining forest and 577.58 seeds.m -2 in the pasture distant 80-100m from the remaining forest. At the soil seed bank evaluation in the experimental area inside the Citrus sp crop, the ruderal species were 99.88% of the germinated species in the rainy season and 99.73% in the dry season. In the experimental area inside the pasture, for the rainy season, 100% of the germinated species were herbal species typically ruderal in both distances; in the soil collected in the dry season, this life form was predominant in 99.66% and 99.92% in both distances, respectively. In the saplings counting, a 5.8 ind.m -2 density inside was found the Citrus sp crop and 1.2 and 2.2 ind.m -2 inside the pasture in both distances. Only for the seeds rain significant differences were found between the Citrus sp crop and the pasture. No significant differences were found between the two distances within the pasture area strips, denying the hypothesis that the resilience of the study area is inversely related to the remaining forest distance.

Ações de recuperações de áreas degradadas têm sido amplamente empregadas, tanto por exigências legais como por iniciativas de grupos preocupados com a qualidade ambiental, assim não havendo uma padronização destas ações. Surgindo então a necessidade de avaliar se as metodologias empregadas estão alcançando seu objetivo e proporcionando uma auto-sustentação da comunidade florestal formada. O presente trabalho teve como objetivo descrever a comunidade arbustivo-arbórea de uma área restaurada, por meio de um plantio com alta diversidade, após 18 a 20 anos de sua implantação. O estudo foi desenvolvido em uma Floresta Estacional Semidecidual (FES) no município de Iracemápolis estado de São Paulo Sudeste do Brasil (22°35\'S e 47°31\'W). O clima regional é do tipo Cwa segundo a classificação de Köppen, com precipitação variando de 1.100 a 1.700mm por ano. O plantio foi realizado entre 1988 e 1990, em aproximadamente 50ha. Foi realizado um levantamento florístico e fitossociológico de duas áreas com 1,0ha cada, foram amostrados todos os indivíduos com perímetro a altura do peito igual ou maior que 10cm para calculo dos parâmetros fitossociológicos e dos índices de diversidade e de equidade. As espécies amostradas foram classificadas quanto a classe sucessional e a síndrome de dispersão. Foi verificada fisionomia florestal nas duas áreas estudadas. Foram encontrados 2.532 indivíduos vivos, distribuídos em 52,05% na área 1 e 47, 95% na área 2, e estavam distribuídos em 143 espécies, compondo 40 famílias. A altura do dossel foi inferior ao encontrado em remanescentes de FES, porém os índices de diversidade e equidade, bem como a densidade absoluta estiveram entre os valores obtidos para FES. As espécies que apresentaram maior crescimento foram Lafoensia glyptocarpa, Melia azedarach, Pterocarpus violaceus, Centrolobium tomentosum, Cariniana estrellensis, Triplaris americana, Cariniana legalis e Balfourodendron riedelianum na área 1 e Luehea divaricata, Pterogyne nitens, Citharexylum myrianthum e Triplaris americana na área 2. Foram verificados indivíduos com forma de vida vegetais diferentes dos introduzidos assim como espécies arbustivo-arbóreas diferentes das implantadas. A maior parte dos indivíduos regenerantes foi de espécies secundárias iniciais e pioneiras, sendo que as maiores espécies, tanto em altura como em área basal, foram provenientes das espécies plantadas. As duas áreas foram consideradas como restauradas e apresentam características de vegetação secundária. A composição inicial das espécies utilizadas e suas classes sucessionais influenciaram a composição da floresta formada com 18 e 20 anos. A utilização de alta diversidade em plantios de restauração apresenta-se de grande importância para o restabelecimento da estrutura, possibilitando o desenvolvimento dos processos existentes em florestas naturais nas áreas restauradas, especialmente em áreas não conectadas a fragmentos florestais naturais. / Restoration actions in degraded areas have been widely used, as much for legal requirements as for initiatives of groups worried about the ambient quality, in this way not having an standardizing of this actions. Appearing the necessity to evaluate if the employed methodologies are reaching its objective and providing a self-sustentation of the formed forest community. The present work had as objective to describe the community of tree and shrub from restored area, by a high diversity plantation, after 18 and 20 years of your implementation. The study was developed in Semideciduous Seasonal Forests (FES) at Iracemápolis City in São Paulo, Southeastern of Brazil (22°35\'S and 47°31\' W). The regional climate is Cwa, according to Köppen classification, with precipitation varying from 1.100 to 1.700mm per year. The plantation was realized between 1988 and 1990, in approximately 50ha. It was realized a floristic and phytosociological survey from two areas with 1,0ha each, where had been sampled individuals with perimeter at breast height equal or bigger than 10cm for calculate phytosociological parameter and diversity indices of equability. The showed species had been classified according to sucessional class and the syndrome of dispersion. Forest physiognomy was verified in the two studied areas. It has been found 2,532 individuals alive, distributed in 52,05% at area 1 and 47, 95% at area 2, and were distributed in 143 species, composing 40 families. The canopy heights had been less than found in FES remained, however, the diversity and equability index, and the absolute density has been among the value obtained to FES. The species that had presented greater growth had been Lafoensia glyptocarpa, Melia azedarach, Pterocarpus violaceus, Centrolobium tomentosum, Cariniana estrellensis, Triplaris americana, Cariniana legalis and Balfourodendron riedelianum in the area 1 and Luehea divaricata, Pterogyne nitens, Citharexylum myrianthum and Triplaris americana in area 2. Had been verified individuals with different vegetal life forms from introduced species as well as tree and shrub species different from implemented. Most of the regenerate individual was from pioneering and initial secondary species, and the biggest species, in height and in basal area had been coming from the planted species. It is concluded that the two areas are restored and present characteristic of secondary vegetation, the initial composition from used species and respective sucessional class had influenced the forest composition formed with 18 and 20 years. The use of high diversity in plantations of restoration present with high importance to re-establishing of the structure, enabling the development of existing process in a natural forests, especially in areas not connected with fragments of natural forests.

In Florida, mangroves have responded to climate change by slowly migrating northward into traditional salt marsh habitat. However, little is understood about the relationships among mangrove growth form plasticity and environmental conditions. In addition, the effects of the mangrove northward expansion on pre-existing salt marsh communities are unknown, especially any influences of differences in tree morphology. The size, canopy structure, and root structure of the three mangrove species Rhizophora mangle, Avicennia germinans, and Laguncularia racemosa were measured at six sites along the east coast of Florida. Structural equation modeling was used to evaluate the multivariate relationships between environmental and biotic variables. Mangrove growth form varied widely with environmental variables. The results of this study suggest that R. mangle expansion into salt marsh may rely on interactions with salt marsh and shading as well as on climatic variables, which has implications for future mangrove expansion northward in Florida. / Includes bibliography. / Thesis (M.S.)--Florida Atlantic University, 2016. / FAU Electronic Theses and Dissertations Collection

O presente trabalho teve como objetivo investigar a resiliência de uma área desflorestada há aproximadamente 20 anos, ocupada atualmente com pastagem e cultivo de Citrus sp. Essa resiliência foi avaliada através dos seguintes aspectos da dinâmica florestal: análise do banco de sementes, da chuva de sementes e de indivíduos jovens regenerantes. Este trabalho foi conduzido no Parque Estadual do Jurupará (23°51' S e 47°11' W), abrangendo os municípios paulistas de Ibiúna e Piedade, em uma região de transição entre a Floresta Ombrófila Densa e a Floresta Estacional Semidecidual. Foram alocadas três faixas de amostragem, cada uma com cinco parcelas aleatorizadas de 10 X 20 m, uma num trecho ocupado com um plantio abandonado de Citrus sp, adjacente ao remanescente florestal, e as restantes num trecho ocupado com pastagem, uma a 0-20 m e outra a 80-100 m de distância do remanescente florestal. Para a avaliação da chuva de sementes, foram lançados aleatoriamente em cada parcela três coletores de sementes circulares de 0,52 m de diâmetro, com coletas mensais das sementes depositadas. Para a avaliação do banco de sementes foram instalados em cada parcela, três subparcelas de 0,25 X 0,25 m, para coleta de solo até 0,05 m de profundidade em duas épocas distintas: estação chuvosa (janeiro/2001) e na estação seca (agosto/2001). Para a avaliação dos indivíduos jovens regenerantes, foram implantadas aleatoriamente 4 subparcelas de 0,5 X 0,5 m, nas quais foram realizadas três avaliações de todos os indivíduos arbustivos-arbóreos com altura entre 0,30 e 1,30 m. Na avaliação da chuva de sementes na área ocupada com o cultivo de Citrus sp, foi observada alta densidade de sementes autóctones de espécies arbustivo-arbóreas (Leandra sp. com 20.638,73 sem.m -2 e Tibouchina sp. com 12.681,85 sem.m -2 ) que ocupavam a área junto com aos indivíduos de Citrus sp. Na pastagem verificou-se a predominância de espécies ruderais, a densidade média das espécies arbustivo-arbóreas foi de 335,75 sem.m -2 , na pastagem próxima do remanescente florestal e de 577,58 sem.m -2 na pastagem distante do remanescente florestal. Na avaliação do banco de sementes no cultivo de Citrus sp, as espécies ruderais consistiram em 99,88% das espécies germinadas na estação chuvosa, e 99,73% na estação seca. Na pastagem, na estação chuvosa, para as duas distâncias, 100% das espécies germinadas eram espécies herbáceas tipicamente ruderais; na estação seca esta forma de vida predominou em 99,66% na área próxima ao remanescente florestal e 99,92% na área mais distante. No levantamento dos indivíduos jovens regenerantes, encontrou-se densidade 5,8 ind.m -2 na área de Citrus sp e de 1,2 ind.m -2 e 2,2 ind.m -2 na pastagem a 0-20 m e 80-100 m de distância do remanescente florestal, respectivamente. Apenas na chuva de sementes foram encontradas diferenças significativas entre a área de Citrus sp e a pastagem, para os demais aspectos analisados não foram encontradas diferenças significativas entre a área de Citrus sp e pastagem. Na pastagem, para todos os apectos analisados, não foram encontradas diferenças significativas entre as diferentes distâncias, rejeitando a hipótese de que a resiliência da pastagem estudada está inversamente relacionada com as distâncias do remanescente florestal nesse trabalho. / This work had as a goal identifying the resilience of an area, which was deforested in the past, currently used as pasture and Citrus sp crop. This resilience was evaluated through the following aspects of forest dynamics: soil seed bank analysis, seed rain and saplings. It was conducted in the Jurupará State Park in Ibiúna and Piedade (São Paulo State), in a transition area between the Ombrophil Forest and the Semideciduous Seasonal Forest. In this area, three sampling strips were allocated, each one with five 10 X 20 m plots, being one inside the Citrus sp crop and the others inside the pasture, distant 0-20 m and 80-100 m from the forest remant. For evaluating the seed rain, three circular seeds collectors of 0.52 cm in diameter were randomly set in each plot, with monthly samplings of the deposited seeds. For evaluating the seed bank, soil of three 0.25 X 0.25 m sub-plots and 0.05 m deep was collected in two different seasons: rainy season (January/2001) and dry season (August/2001). To the saplings evaluation, four 0.5 X 0.5 m sub-plots were implanted randomly, in which three evaluations of all the shrubs and trees individuals (0.30-1.30m height) were performed. At the seed rain inside the Citrus sp crop, a high density of autoctone seed of shrubs and trees species (Leandra sp. with 20,638.73 seed.m -2 and Tibouchina sp. with 12,681.85 seeds.m -2 ) was observed; inside the pasture, there were a predominance of ruderal species, while the average density of shrubs and trees species were, 335.75 seeds.m -2 in the pasture distant 0-20m from the remaining forest and 577.58 seeds.m -2 in the pasture distant 80-100m from the remaining forest. At the soil seed bank evaluation in the experimental area inside the Citrus sp crop, the ruderal species were 99.88% of the germinated species in the rainy season and 99.73% in the dry season. In the experimental area inside the pasture, for the rainy season, 100% of the germinated species were herbal species typically ruderal in both distances; in the soil collected in the dry season, this life form was predominant in 99.66% and 99.92% in both distances, respectively. In the saplings counting, a 5.8 ind.m -2 density inside was found the Citrus sp crop and 1.2 and 2.2 ind.m -2 inside the pasture in both distances. Only for the seeds rain significant differences were found between the Citrus sp crop and the pasture. No significant differences were found between the two distances within the pasture area strips, denying the hypothesis that the resilience of the study area is inversely related to the remaining forest distance.

O presente trabalho investiga a rede social composta por organizações envolvidas na problemática da recuperação florestal na Mata Atlântica no Estado de São Paulo (Brasil). A recuperação de áreas degradadas é um dos principais desafios para cientistas, poder público e todos os atores sociais que buscam reverter o processo de destruição das florestas naturais. Com o aprimoramento da legislação ambiental, a rede de atores sociais torna-se densa e os conflitos entre eles tornam-se mais explícitos em diferentes “arenas de disputa", que são espaços de negociação, de conflitos e de mobilização social. A pesquisa confirma a hipótese de que apenas a mudança de paradigma científico na Ecologia de Restauração não é suficiente para garantir a qualidade de projetos de recuperação de áreas degradadas, sendo necessários uma estrutura de incentivos que estimule o fluxo de informações da rede social, a organização do setor de sementes de espécies florestais nativas, o melhor uso dos recursos florestais das unidades de conservação e a permanente negociação entre os atores sociais envolvidos em projetos de recuperação de áreas degradadas. / The present work investigates the social network composed by organizations involved in the problematic inquiries on forest recovering of Rainforest in São Paulo State (Brasil). The recovering of degraded areas is one of the main challenges for the scientists, the public government, and all the social actors that look forward to reversing the destruction process of natural forests. As the environmental laws improve, the social network actors become dense and the conflicts among them become more and more explicit in different “arena of debate", which are spaces for negotiation, conflicts and social mobilization. The research confirms the hypothesis that only changes in the scientific paradigm on Restoration Ecology is not enough to assure the quality of projects on recovering of degraded areas. In order to do so, a structure with incentives that stimulates the flow of social network information, the organization on the native forest seeds section, the best use of forest resources on the conservation units and the steady negotiation among the social actors involved in projects on recovering the degraded areas is necessary.

Refazer ecossistemas de forma artificial representa um desafio de iniciar um processo de sucessão o mais semelhante possível aos processos naturais. A recuperação ambiental tem se baseado no modelo da silvicultura tradicional, plantandose árvores sob espaçamento 3 x 2 m, em área total, com altos insumos de implantação/manutenção, e gerando-se bosques desenvolvidos em altura, porém com baixa diversidade de formas de vida e regeneração. Técnicas nucleadoras de restauração formam microhabitats em núcleos propícios para a chegada de uma série de espécies de todas as formas de vida, que num processo de aceleração sucessional, irradiam diversidade por toda a área. As técnicas foram implantadas em áreas piloto de um hectare, denominadas "Unidades Demonstrativas" (UDs). As UDs foram montadas em Floresta Estacional Semidecidual (Capão Bonito-SP), Cerrado (Santa Rita do Passa Quatro-SP) e Restinga (Florianópolis-SC). Na primeira UD, com um ano de idade, as técnicas nucleadoras introduziram 1.603 mudas de 148 espécies nativas, dentre 84 espécies arbóreas (883 mudas), 12 arbustivas (124 mudas), 30 herbáceas (242 mudas), 20 trepadeiras (260 mudas) e 2 bromeliáceas (3 mudas), além de 94 mudas de hábito indeterminado. Entre as espécies, ocorreram 69 zoocóricas, 32 autocóricas e 29 anemocóricas, além de 21 plantas indeterminadas. Desconsiderando-se as 47 espécies arbóreas implantadas por mudas, houve introdução de: 25% de arbóreas, 8% de arbustos, 20% de ervas, 14% de lianas e 1% de bromeliáceas. Na UD de Cerrado, apesar de impactada por gado, aos dois anos de idade, foram introduzidos 354 indivíduos de 31 espécies nativas. Destas, 39% foram espécies arbóreas, 13% arbustivas, 16% herbáceas, 16% lianas e 16% indeterminadas. Foram registradas 35% de espécies zoocóricas, 29% de anemocóricas, 19% de autocóricas e 16% de plantas com síndrome indeterminada. Na UD de Restinga, foram detectadas, aos dois anos e meio de idade, 180 espécies de 108 gêneros e 55 famílias. As técnicas nucleadoras resultaram num custo experimental estimado em torno de 34% mais barato em relação ao modelo tradicional que varia em torno de R$ 5.500,00 reais/ha. O uso da nucleação aumentou nitidamente a eficiência da restauração ecológica. Foi restituída a diversidade, não só em seu aspecto estrutural, mas considerando-se também os diferentes nichos, formas e funções, formando um mosaico de ambientes e permitindo uma maior dinâmica das comunidades. No atual estágio de conhecimento, é importante a definição de qual paradigma almejamos para a restauração de nossas florestas: cultivar plantações de árvores nativas ou permitir e acelerar a sucessão natural? O novo paradigma das técnicas nucleadoras, ao contrário dos modelos tradicionais de recuperação que apenas satisfazem exigências legais, promovem a restituição de produtores, consumidores e decompositores, gerando a conservação efetiva dos ecossistemas, e assumindo, desta forma, um compromisso ético com as futuras gerações. / To remake ecosystems of artificial form represents a challenge to initiate a process of the possible most similar succession to the natural processes. The environmental recuperation has based on the model of traditional forestry, standing trees under 3 x 2 m spacing, in total area, with high implantation/ maintenance inputs, and generating forests developed in height, however with low diversity of forms of life and regeneration. Restoration nucleation techniques form microhabitats in nuclei propitious for the arrival of a series of species of all the life forms that in a process of sucessional acceleration, radiate diversity for all the area. The techniques had been implanted in pilot areas of one hectare, called "Demonstrative Units" (UDs). The UDs had been mounted in seasonal semidecidual forest (Capão Bonito-SP), Brazilian savanna (Santa Rita do Passa Quatro-SP) and coastal plain vegetation (Florianópolis-SC). In the first UD, with one year of age, the nucleation techniques had introduced 1,603 seedlings of 148 native species, amongst 84 arboreal species (883 seedlings), 12 shrubs (124 seedlings), 30 herbaceous ones (242 seedlings), 20 lianas (260 seedlings) and 2 bromelias (3 seedlings), in addition to 94 seedlings of indeterminate habit. Among the species, 69 zoochore, 32 autochore and 29 anemochore had occurred, plus 21 indetermined plants. Disrespecting the 47 arboreal species implanted by traditional seedlings, there was introduction of: 25% of arboreal, 8% of shrubs, 20% of herbaceous, 14% of lianas and 1% of bromelias. In Brazilian savanna UD, although affected by cattle when two years of age, 354 individuals of 31 native species had been introduced. Of these, 39% had been arboreal species, 13% shrubs, 16% herbaceous, 16% lianas and 16% indetermined. There had been registered 35% of zoochore species, 29% of anemochore, 19% of autochore and 16% of plants with indetermined syndrome. In coastal plain vegetation UD, in two years and half of age, 180 species of 108 genus and 55 families had been detected. The nucleating techniques had resulted cheaper in an esteemed experimental cost around 34% in relation to the traditional model that varies around R$ 5,500.00 reais/ha. The use of the nucleation clearly increased the efficiency of the ecological restoration. The diversity not only restituted its structural aspect, but also the different niches, forms and functions, forming an environment mosaic and allowing a dynamic growth of the communities. In the current period of knowledge, is important the definition of which paradigm we wish for the restoration of our forests: to cultivate plantations of native trees or to allow and to speed up the natural succession? The new paradigm of the nucleation techniques, in contrast to the traditional models of recovery that only satisfy legal requirements, replenishes the producers, consumers and decompositors, promoting the conservation of the ecosystems, and adopting an ethical commitment with the future generations.

5 Absctract Environment and demographic characteristics of host population are important factors affecting incidence and severity of plant diseases. The aim of this study was to reveal possible effects of microclimatic and edaphic characteristics and host population demographic factors on the biotrophic pathogen Puccinia cribrata, microcyclic rust parasitising clonal evergreen plant Vinca minor. I studied the ecology of this pathosystem in natural populations of V. minor in the Soča valley in the Julian Alps in Slovenia. Rugged terrain of the Soča valley with different bedrocks allowed to study pathogen distribution at topographically diverse forest and scrub sites, greatly differing in soil depth and canopy structure. P. cribrata was significantly more likely to occur in the themophilous forest with shallow calcareous soils and open canopy than in the mesophilous forest types. Its prevalence (proportion of diseased stems in population) was also highest in this type of vegetation. Most important host population factors were population size and population density positively affecting incidence and prevalence respectively. Additionally, I tested various vegetation and topographic indexes derived from remote sensing for usability in prediction models. It appears that vegetation indexes connected with canopy...

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[Truncated abstract] Mediterranean southwest Australia, a global biodiversity hotspot, has nutrient deficient soils, exacting climatic conditions and is species rich with 7380 native vascular plant species, of which 49% are endemic. The region is expected to experience one of the world's highest degrees of biodiversity loss and change in the coming decades, with introduced species presenting a major threat. Limited knowledge is available on the mechanisms of ecosystem change associated with invasion and fire in this biodiversity hotspot region. Banksia woodland, an iconic complex species-rich natural ecosystem is one of the major vegetation types of the coastal sandplain, extending from 15 to 90 km inland and 400 kms along the west coast. The following hypothesis was tested to explore the ecological impacts of invasion: Is invasion of Banksia woodland by the introduced species Ehrharta calycina and Pelargonium capitatum accompanied by an alteration in ecosystem properties and processes, whereby the degree of change is related to fire frequency and abundance of introduced species? Different vegetation conditions, i.e. Good Condition (GC), Medium Condition (MC), Poor Condition invaded by Ehrharta calycina (PCe) and Poor Condition invaded by Pelargonium capitatum (PCp) were utilized for field assessments. ... In the soil seed bank, species numbers and germinant density decreased significantly for native and seeder (fire sensitive) species between GC sites and invaded sites. Surprisingly 52% of germinants at GC sites were from introduced species, with much of the introduced soil seed bank being persistent. Native species were dominated by perennial shrubs, herbs and sedges, while introduced species were dominated by perennial and annual grasses and herbs. Invasion by introduced species, associated with frequency of fire, altered the ecosystem, thus disadvantaging native species and improving conditions for even greater invasion within the Banksia woodland. Significantly higher soil phosphorus P (total) and P (HCO3) were found at PCe and PCp sites compared to GC sites. Leaf nutrient concentrations of phosphorus were significantly higher, and potassium and copper significantly lower in PCe and PCp sites, with introduced species having significantly greater concentrations than native species (except Manganese). This study demonstrated the key role of phosphorus in the Banksia woodland, in contrast to other research which identified nitrogen as the major nutrient affected by invasion. Higher levels of soil and leaf phosphorus, loss of species diversity and function, changes in fire ecology and canopy cover and a limited native soil seed bank make restoration of a structural and functional Banksia woodland from the soil seed bank alone unlikely. Without management intervention, continuing future fire is likely to result in a transition of vegetation states from GC to MC and MC to PC. The knowledge gained from this study provides a better ecological understanding of the invasive process. This enhanced understanding will enable the development of adaptive management strategies to improve conservation practices within a biodiversity hotspot and reduce the impact of the key threatening process of invasion.

This study investigated the utility to vertebrates of upland linear riparian rainforest fragments on the Atherton and Evelyn Tablelands in the Australian Wet Tropics region, north Queensland. Similar linear fragments were selected, that varied in forest age and their connectivity to large areas of continuous forest:- (connected primary (N=6), isolated primary (N=5), connected secondary (N=6) and isolated secondary (N=7)). Primary sites had either never been cleared or only subject to selective logging, while secondary forest had been completely cleared and allowed to regenerate for at least 30 years. These linear fragments were contrasted with riparian sites within continuous forest sites (N=6 to 7), which were situated in State Forest or National Parks, and sites within the cleared matrix (pasture, N=6). Vertebrates surveyed were birds, ground-dwelling mammals and reptiles, particularly leaf-litter skinks. All surveys were conducted between September and December in 2001 and/or 2000. Chapter 2 investigates the effects of forest age, isolation and structural vegetation features on bird assemblages within linear riparian fragments of rainforest. Bird surveys and structural vegetation assessments were conducted within connected and isolated primary and secondary linear fragments, and compared with those of continuous forest habitat (N=6) and pasture. There were strong effects of forest age; all three types of primary rainforest had higher values than secondary rainforest for most measured attributes of vegetation structure (including canopy height and cover; and frequency of large-diameter trees, lianes, epiphytes, strangler figs; and woody debris), but lower frequencies of tree ferns and thorny scramblers. Sites within primary rainforest also had a greater frequency of many bird species across different guilds of habitat, feeding and movement. Assemblages of rainforest-dependent birds showed an effect of isolation, although its strength was less than that of forest age. Isolated fragments of primary rainforest differed significantly from continuous primary rainforest in their rainforest-dependent bird species assemblages (and had lower species richness), and isolated fragments of secondary rainforest differed from those that were connected. There was a significant association between the species composition of rainforest birds and some measured vegetation parameters across all sites, but not within primary or secondary sites. Vegetation differences did not explain the lowered frequency of several species in isolated fragments. Limited dispersal seems unlikely to be a main cause, and causal processes probably vary among species. Specialist rainforest species endemic to the Wet Tropics region showed stronger responses to present-day rainforest age and fragmentation than those not endemic. Variation in nest depredation levels associated with rainforest fragmentation (edge effects) is examined in Chapter 3. Artificial nests were placed in the forest understorey at seven edge sites where continuous forest adjoined pasture, seven interiors (about one kilometre from the edge), and six primary linear riparian forest remnants (50-100 m wide) that were connected to continuous forest. Four nest types were compared, representing different combinations of two factors; height (ground, shrub) and shape (open, domed). At each site, four nests of each type, containing one quail egg and two model plasticine eggs, were interspersed about 15 m apart within a 160 m transect. Predators were identified from marks on the plasticine eggs. The overall depredation rate was 66.5% of 320 nests' contents damaged over a three-day period. Large rodents, especially the rat Uromys caudimaculatus, and birds, especially the spotted catbird Ailuroedus melanotis, were the main predators. Mammals comprised 56.5% and birds 31.0% of identified predators, with 12.5% of unknown identity. The depredation rate did not vary among site-types, or between open and domed nests, and there were no statistically significant interactions. Nest height strongly affected depredation rates by particular types of predator; depredation rates by mammals were highest at ground nests, whereas attacks by birds were most frequent at shrub nests. These effects counterbalanced so that overall there was little net effect of nest height. Mammals accounted for 78.4% of depredated ground nests and birds for at least 47.4% of shrub nests (and possibly up to 70.1%). The main predators were species characteristic of rainforest, rather than habitat generalists, open-country or edge specialists. For birds that nest in the tropical rainforest understorey of the study region, it is unlikely that edges and linear remnants presently function as ecological population sinks due to mortality associated with increased nest depredation. The use of linear riparian remnants by small ground-dwelling mammals and reptiles (mainly leaf litter skinks), is reported in Chapter 4. Site types were continuous rainforest, connected and isolated linear fragments of both uncleared primary rainforest and secondary regrowth rainforest. Mammals were also surveyed in pasture sites. Neither reptile species richness nor abundance varied significantly among site types. Although mammal species richness varied significantly between site types, with isolated primary sites containing highest species richness, overall mammal abundance did not differ significantly among site types. Pasture sites differed significantly from all rainforest sites in their mammal species composition, and were dominated by the introduced house mouse (Mus musculus). This species was absent from all rainforest sites, which were characterised by moderate abundances of bush rat/Cape York rat Rattus fuscipes/leucopus, fawn-footed melomys Melomys cervinipes and giant white-tailed rat Uromys caudimaculatus. None of these species varied significantly in abundance among site types, although the giant white-tailed rat showed a trend (P=0.09) for reduced abundance in isolated secondary sites. A single reptile species, the prickly forest skink Gnypetoscincus queenslandiae, occurred in sufficient numbers for individual analysis, and its abundance varied significantly among the forested site types, being less abundant in all linear fragments than in continuous forest sites. The utility of linear riparian rainforest for vertebrates appears to be species-specific and involves many factors. However, overall, species endemic to the Wet Tropics (which are hence of the highest conservation significance) appear to be the most sensitive to fragmentation. These species were most likely to show altered abundances or frequencies of occurrence due to isolation, forest age, and habitat linearity. The ecology of species within this group warrants further investigation within fragmented and non-fragmented regions of the Tablelands. For many other vertebrates examined in this study, there appears to be sufficient functional connectedness between remnants on the Tablelands to minimise the effects of fragmentation. Nevertheless, the lower density of many of these species in pasture may indicate that their long-term persistence within the fragmented rainforest areas could benefit from the maintenance or establishment of habitat linkages. Certainly, if the current rainforest vegetation cover were further reduced, or if the land use in the matrix became more intensive, the establishment of specific habitat linkages could become more important as existing dispersal routes could be lost. It also appears that nest depredation levels are unlikely to limit the value of linear rainforest remnants and other small rainforest remnants as breeding habitat for birds (at least for understorey-nesting species), relative to more intact rainforest, in the study region.