Background: Venomous snakebite and its effects are a source of fear for people living in southern Nepal. As a result, people have developed a negative attitude towards snakes, which can lead to human-snake conflicts that result in killing of snakes. Attempting to kill snakes increases the risk of snakebite, and actual killing of snakes contributes to loss of biodiversity. Currently, snake populations in southern Nepal are thought to be declining, but more research is needed to evaluate the conservation status of snakes. Therefore, we assessed attitudes, knowledge, and awareness of snakes and snakebite by Chitwan National Park's (CNP) buffer zone (BZ) inhabitants in an effort to better understand challenges to snake conservation and snakebite management. The results of this study have the potential to promote biodiversity conservation and increase human health in southern Nepal and beyond. Methods: We carried out face-to-face interviews of 150 randomly selected CNP BZ inhabitants, adopting a cross-sectional mixed research design and structured and semi-structured questionnaires from January-February 2013. Results: Results indicated that 43 % of respondents disliked snakes, 49 % would exterminate all venomous snakes, and 86 % feared snakes. Farmers were the most negative and teachers were the most ambivalent towards snakes. Respondents were generally unable to identify different snake species, and were almost completely unaware of the need of conserve snakes and how to prevent snakebites. Belief in a snake god, and the ability of snakes to absorb poisonous gases from the atmosphere were among many superstitions that appeared to predispose negativity towards snakes of BZ residents. Conclusion: People with predisposed negativity towards snakes were not proponents of snake conservation. Fear, negativity, ambivalence towards, and ignorance about, snakes and the need for snake conservation were strong indicators of the propensity to harm or kill snakes. It seems that if wanton killing of snakes continues, local snake populations will decline, and rare and endangered snake species may even become locally extirpated. Moreover, inappropriate perception and knowledge about snakes and snakebites may put BZ people at increased risk of venomous snakebite. Therefore, intensive, pragmatic educational efforts focused on natural history and ecology of snakes and prevention of snakebite should be undertaken in communities and at schools and universities.

The distribution of species in space is determined by the species dispersal capacity, adaptation to environmental conditions, and response to predators and competitors. To determine the importance of dispersal limitation, environmental filtering, and species interactions on the distribution of species in the Brazilian Amazonian forest, I sampled termites in a large area of Brazil. I investigated patterns in species occurrence that could indicate competition and predation structuring termite communities, and analyzed the association of termite abundance and species richness with the density of ant predators. The spatial distribution of termites, and their association with climatic and edaphic conditions were also used to infer about the effects of dispersal limitation and environmental filtering. A total of 271 termite species and 4,389 colonies was found in the 148 transects sampled. Predator density was the strongest predictor of termite abundance and species richness at small spatial scales, but the turnover in termite species composition was mostly associated with measures of soil texture. At broad spatial scales, soil chemistry, climate, and isolation by distance were associated with termite abundance, species richness, and species composition. These results suggest that both species interactions, their association with the environment, and their dispersal capacity determine their distribution. Nevertheless, dispersal limitation seem to be stronger over large areas, whereas environmental filtering can act both at small and large geographic scales.

The aim of this diploma thesis is to compare natural and human-influenced malacocenoses in the vicinity of the villages Krasíkov and Domaslav in the district of Tachov, Czech Republic. Inventory research was conducted between 2012 and 2013. A total of 36 gastropod species were found, and a total of 1088 snail shells were collected. On some of the surveyed sites (the farm Krasíkov, Domaslav, the pond near Ovčí vrch) the influence of anthropic stress is evident. Four species found during this study are also listed in the Red List of Threatened Species of the Czech Republic (Aegopinella nitidula, Balea perversa, Ena montana, Vertigo pusilla). Based on the results of the research, two variants of the didactic use of a such malacological research were created in the teaching of natural science and biology. Keywords: Mollusca, Gastropoda, malacocenosis, species diversity, ecology of mollusk assemblages, Krasíkov.

Student Number : 9907276D - MSc Dissertation - School of Animal, Plant and Environmental Sciences - Faculty of Science / The broad aim of this study was to measure the ecosystem repair of the Sabie River (which traverses through both the grassland and savanna biomes) riparian environment in Mpumalanga, South Africa, in response to the clearing of alien plants by the Working for Water (WfW) alien plant clearing programme. This was done in order to assess the effectiveness of the WfW clearing on the Sabie River riparian plant community composition and associated environmental factors. Although “effectiveness” can be assessed in various ways, in this study it included determining whether there was a reduction in the invasion intensity (defined as the percentage aerial cover of woody alien plants) after clearing. This broad aim was achieved by studying the impacts of the WfW alien plant clearing programme, as well as the invasion of alien plants, on the plant species composition, diversity and vegetation structure of riparian ecosystems on the Sabie River. Hence, in 2005 40 modified Whittaker nested plots were sampled. The impacts on the Sabie River riparian environment were also assessed by measuring various environmental variables that are likely to change as a result of clearing, such as the ground cover (percentages of exposed soil, rock, litter, herbaceous vegetation and grass), as well as various soil chemical and physical properties. Twenty plots were surveyed along the Sabie River in the Hazeyview region (savanna biome), ten in the Sabie region (grassland biome) and ten in the Graskop region (grassland biome). The response of the Sabie River riparian community to invasive alien plant clearing by WfW (and the alien plant invasion itself) was also assessed over time, by comparing the 2005 study with one done in 1996, which used the same plots. In 2005, a cumulative total of 282 species were found, 222 (79%) of which were indigenous and 60 (21%) alien. The grassland sites had a higher cumulative total of 222 species compared with the 171 species in the savanna sites. A total of 112 (39%) species were common between the biomes, 86 (30%) of which were indigenous and 26 (9%) alien. At the 1000 m2 scale, the indigenous species richness (32.4 ± 1.4 (S.E.)) was significantly higher than the alien species richness (12.0 ± 0.5) (P < 0.001). Of the 60 alien species, 17 (28%) were shrubs and 15 (25%) trees. The grassland sites were more species rich at the 1000 m2 scale (48.8 ± 1.8) and diverse at the 100 m2 scale (Simpson’s index of alpha diversity of 0.90 ± 0.01) than the savanna sites (species richness of 40.0 ± 2.1 and alpha diversity of 0.85 ± 0.02; P = 0.003 for species richness and P = 0.04 for alpha diversity). The Sabie sites were more species rich at the 1000 m2 scale (52.6 ± 2.8) than the Graskop sites (45.0 ± 1.4) (P = 0.12). The higher species richness in the Sabie region contributed to the higher total species richness in the grasslands relative to the savanna sites. At the 1000 m2 scale, the overall beta diversity (Sorenson’s coefficient of community) between the biomes was 0.57, and the species complementarity (the Marczewski-Steinhaus distance) between the biomes was 0.60, indicating that the biomes were not that similar in terms of species composition. Even though the grassland was more rich and diverse in terms of species than the savanna, the overall relative abundances of plant species in each biome was very similar (species evenness (Simpson’s measure of evenness), at the 100 m2 scale, of 0.52 ± 0.03 in the grassland and 0.51 ± 0.03 in the savanna; P = 0.74). The savanna tended to have a higher degree of invasion intensity (aerial cover of woody alien plants of 34.4 ± 4.6% compared to 29.4 ± 4.5% in the grassland; P = 0.44), possibly due to its position lower in the catchment, and hence a sink for upstream alien plant propagules. It was hypothesized that higher plant species richness and/or diversity should enhance community resistance to alien plant invasions, in both the grassland and savanna biomes. In the Sabie (grassland) region, there was a negative correlation between the indigenous and alien species richness, thus indicating that the Sabie region plant community may have been more resistant to the invasion of alien plants than the other two regions. Therefore, the hypothesis was not rejected for the Sabie region. On the other hand, in the Graskop (grassland) and Hazeyview (savanna) regions, there were positive correlations between the indigenous and alien species richness, thus indicating that these plant communities may not have been as resistant to the invasion of alien plants. Therefore, the hypothesis was rejected for both the Graskop and Hazeyview regions. When considering the biome scale, the hypothesis was not rejected as the increase in total species richness with increasing invasion intensity in the grassland (which was more diverse than the savanna) indicated that it may have been more resistant to the invasion of alien plants than the savanna, which had a total species richness that decreased with increasing invasion intensity. In 2005, exposed soil, litter and grass covers tended to be slightly higher in the savanna (14.4 ± 1.6%; 43.5 ± 3.0%; 21.8 ± 1.7% respectively) than in the grassland (12.1 ± 2.5%; 43.2 ± 4.2%; 20.1 ± 2.3% respectively) (P = 0.43, 0.96 and 0.56 respectively). Rock and herbaceous covers were higher in the grassland (4.3 ± 1.6% and 20.3 ± 1.7% respectively) than in the savanna (0.8 ± 0.2% and 19.5 ± 2.2% respectively), but only rock cover was significantly different (P = 0.04) (P = 0.76 for herbaceous cover). These patterns in ground cover may have been a response to the slightly higher invasion intensity in the savanna. The hypothesis that the lower the degree of alien plant invasion, the higher the understorey vegetation cover, which may result in reduced cover of exposed soil and litter, in both the grassland and savanna biomes, was not rejected as the grassland tended to have a lower degree of alien invasion (although not significant), a higher cover of herbaceous vegetation, and corresponding lower covers of exposed soil and litter. The biomes (in 2005) did not differ significantly in soil pH (grassland pH: 4.6 ± 0.1; savanna pH: 4.8 ± 0.1; P = 0.34). However, the grassland soils were generally more fertile than the savanna soils, i.e. higher organic matter (4.5 ± 0.2% versus 3.3 ± 0.4%; P = 0.01) and total nitrogen (0.3 ± 0.02% versus 0.2 ± 0.02%; P = 0.03). The concentrations (mg/l) of most of the nutrients were also higher in the grassland. The lower fertility of the savanna soils may have been related to the higher litter cover of the savanna immobilizing a larger amount of available nutrients than the grassland; another possibility may have been slower rates of soil organic matter decomposition in the slightly cooler (higher altitude) grassland regions. The soils of the grassland sites tended to be more compacted (0.8 ± 0.1 kg/cm2) (but not significantly) than those of the savanna sites (0.7 ± 0.1 kg/cm2) (P = 0.43), and the savanna plots were on significantly steeper ground (12.8 ± 1.7º) than the grassland plots (4.8 ± 1.1º) (P < 0.001), which may have also contributed to lower fertility through greater leaching and erosion losses. From the detrended correspondence analysis (DCA) of the species by plot data, there were no distinct plant communities separating out between the biomes and regions. This is probably because the Sabie River riparian environment essentially supports a riparian forest/woodland, rather than reflecting the species typically found in the adjoining (more upland) grasslands and savannas. Hence, the species composition of the riparian environment was fairly uniform throughout the study area. The canonical correspondence analysis (CCA), which also incorporates the environmental variables, showed that altitude, exposed soil cover, soil pH, organic carbon content and slope steepness were the variables that most closely (and significantly) correlated with the species composition, and two of these variables relate directly to soil fertility, and the other three are indirectly related to soil fertility. Of the original “treatments” of the 1996/1997 study, namely (A) biome (grassland versus savanna), (B) invasion intensity (high (> 50%) versus low (< 50%)), and (C) clearing (cleared versus uncleared), the legacy of the latter two did not persist over time, as there was little or no clear overall relationship between the 1996 and 2005 data when analysed by ANCOVA. The cumulative total species richness sampled in the 40 plots increased from 163 species in 1996, to 282 in 2005 (42% increase). Mean species richness (at the 1000 m2 scale) was 24.1 ± 1.0 in 1996 and 44.4 ± 1.5 in 2005 (P < 0.001). Trees increased from 28 species in 1996 to 46 in 2005 (39% increase), shrubs from 44 to 82 (46%), herbaceous plants from 71 to 121 (41%), and grasses from 20 to 33 (39%). However, even though the species richness of each growth form increased over time, the proportion of each growth form remained approximately the same, i.e. in 1996, 17% of the species were trees, 27% shrubs, 44% herbaceous and 12% grasses; whereas in 2005, 16% were trees, 29% shrubs, 43% herbaceous and 12% grasses. The greatest increase over time was for category 1, 2 and 3 weed species, namely 25 in 1996 to 50 in 2005, a 50% increase. Although mean alpha diversity was higher in 2005 (0.9 ± 0.01 compared to only 0.3 ± 0.03 in 1996 (at the 100 m2 scale); P < 0.001), overall beta diversity over time (a change from 1996 to 2005) was relatively low, indicating a small change in overall species composition, despite the increase in species richness. The invasion intensity (percentage aerial cover of woody alien plants) was similar between the years, i.e. 30.0 ± 4.6% in 1996 and 31.9 ± 3.2% in 2005 (P = 0.73). When comparing the invasion intensity between the three original treatments over time, the invasion intensity of the 1996 grassland and savanna plots remained unchanged. The invasion intensity of the 1996 high invaded plots also remained unchanged over time, however the low invaded plots had a significantly higher invasion intensity in 2005 (P = 0.004). The invasion intensity of the 1996 uncleared plots remained unchanged over time, whereas the cleared plots had a significantly higher invasion intensity in 2005 (P = 0.03). These results clearly show that the legacy of the original invasion intensity and clearing treatments measured in the 1996/1997 study did not persist over time, whereas the inherent differences between the biomes did. The hypothesis that higher plant species richness and/or diversity should enhance community resistance to alien plant invasions was rejected, as both the 1996 and 2005 plant communities were not that resistant to the invasion of alien plants, even though there was a significantly higher species richness and diversity in 2005 than in 1996. It is concluded that because of both the similar growth form composition and invasion intensity over time, the WfW clearing efforts are not succeeding in the primary aim of controlling aliens, particularly woody alien species. However, there was a considerable decrease in the aerial cover of large alien plants, namely (a) alien plants > 5 m decreased from 15.8 ± 4.1% in 1996 to 5.8 ± 1.2% in 2005 (P = 0.02), and (b) those between 2 – 5 m tended to decrease from 13.3 ± 2.8% in 1996 to 11.1 ± 2.4% in 2005 (P = 0.55). However, these decreases were balanced by a considerable increase in the aerial cover of alien plants < 2 m in height, which increased from 3.9 ± 1.0% in 1996 to 15.0 ± 2.1% in 2005 (P < 0.001). This therefore showed that the WfW clearing programme is succeeding, to some extent, in removing most of the larger alien plants but not in controlling the regenerating plants, which recover through post-clearing resprouting and/or newly established seedlings. Exposed soil, rock and litter covers were higher in 2005 (13.3 ± 1.5%; 2.5 ± 0.8%; 43.3 ± 2.5% respectively) than in 1996 (2.1 ± 0.5%; 0.9 ± 0.3%; 16.4 ± 2.7% respectively) (P < 0.001 for soil and litter covers, and 0.07 for rock cover). Herbaceous and grass covers were significantly higher in 1996 (47.8 ± 2.8% and 32.8 ± 2.6% respectively) than in 2005 (20.0 ± 1.4% and 20.9 ± 1.4% respectively) (P < 0.001 for herbaceous and grass covers). These differences in the ground covers between the years may have partially been a response to the major February 2000 flood event, which cleared a large proportion of the vegetation, resulting in much greater rates of erosion and deposition of soils. The WfW clearing operations also removed a significant proportion of the vegetation, and disturbed much that remained, thus modifying the environment. The increase in litter cover may have also been due to the slightly higher invasion intensity in 2005 than in 1996. Soil pH remained unchanged over time (both years had a pH of 4.7 ± 0.1; P = 0.99), indicating that pH was unaffected by the invasion and subsequent clearing of alien plants, as well as the 2000 flood event which moved a tremendous amount of sediment. The hypothesis that the lower the degree of alien plant invasion, the higher the understorey vegetation cover, in both 1996 and 2005, was not rejected as the plots in 1996 had a lower degree of alien invasion (although not significant), a higher cover of herbaceous vegetation, and corresponding lower covers of exposed soil and litter. Along the Sabie River, the alien tree and shrub species with the greatest densities were Rubus cuneifolius (American bramble) (1828 plants/ha), Lantana camara (Lantana) (1760), Solanum mauritianum (Bugweed) (838), Indigofera macrophylla (640), Eucalyptus grandis (Saligna gum) (560), Caesalpinia decapetala (Mauritius thorn) (403), Agrimonia odorata (Agrimonia) (220), Lilium formosanum (St. Joseph’s lily) (218), and Populus x canescens (Grey popular) (125). Focusing the clearing efforts on these species will help to reduce the frequency of re-invasions, reduce costs, and increase ease of clearing. The primary aim of the WfW programme is to increase water supplies by controlling woody alien plants. Therefore, it is concluded that the WfW clearing along the Sabie River has been partially successful, as there has been a significant decrease in the invasion intensity of large (> 5 m) alien trees (which tend to have the highest transpiration rates) over time from 1996 to 2005. In 1996, these large alien trees were represented mainly by Eucalyptus spp. However, the WfW programme was not effective in terms of ecosystem repair, as the invasion intensity increased slightly from 1996 to 2005, largely as a result of the significant increase in the aerial cover of smaller alien shrubs (< 2 m). If left unchecked, these will probably in time result in even higher levels of invasion intensity when the individual plants increase in size and cover. Furthermore, the growth form composition remained relatively unchanged over time, and more than half of the alien species found in 2005 were tree and shrub species. Therefore, little or no ecosystem repair has occurred along the Sabie River. In order to improve the effectiveness of the WfW programme, various detailed recommendations are included, which largely revolve around improvements in follow-up treatments.

A bacia do rio Piracicaba tem recebido atenção especial das autoridades municipais, pois possui grandes problemas de aproveitamento de seus recursos hídricos. A bacia do rio Corumbataí, um dos principais afluentes da margem direita do rio Piracicaba, é regionalmente importante, não só porque ainda possui águas de boa qualidade, mas também por apresentar elementos raros na paisagem do interior do estado. Esta tese teve o objetivo de caracterizar as assembléias de peixes na bacia do rio Corumbataí e fornecer ferramentas para avaliação de seu status ambiental. Foram escolhidos 4 rios principais com 3 pontos de coleta em cada um. Foram realizadas coletas no período de março a junho e setembro a dezembro de 2001, totalizando 24 coletas. Os dados bióticos foram avaliados através de medidas de diversidade. Para testar a hipótese de variação espaço-temporal da assembléia de peixes foi aplicado o modelo linear ANCOVA onde a variável resposta foi a riqueza de espécies; o fator foi ordem do rio; sendo utilizadas 2 covariáveis ambientais: temperatura e número de indivíduos, revelando uma variação espaço-temporal e padrões reconhecidos no meio acadêmico: relação espécie-área e conceito de rio contínuo. Técnicas multivariadas foram aplicadas para determinar a correlação entre a riqueza e a paisagem no entorno do ponto de coleta, revelando que existem mais espécies em locais com maior cobertura vegetal e mata ciliar preservada. Algumas espécies de peixes se mostraram bons indicadores ambientais: Hypostomus strigaticeps, Hoplosternum littorale e Salminus hilarii; por outro lado o Astyanax altiparanae não se mostrou um bom indicador / The Piracicaba river basin has received special attention from local authorities because it has presented a lot of problems about the misutilization of its hydric resources. The Corumbataí river basin, one of the major streams of the right side of the Piracicaba river, is regionally important, not only because it still has good water quality but also because it has unique elements inside the landscape of São Paulo state. This thesis aims to characterize the fish assemblage of the Corumbataí river basin and provide tools to assess the present environmental status of the basin. It has been chosen 4 major streams with 3 unit samples in each one of the streams. The samples were carried out from March to June and from September to December in the year of 2001, making up a total of 24 samples. The biotic data were assessed using diversity measurement. An ANCOVA was used to test the hypothesis of time-space variation of the fish assemblage, where the dependent variable was the species richness; the factor was the stream order and 2 environmental co-variates were used: temperature and number of individuals, thus revealing both time-space variation and some patterns which are recognized academically: species-area relationship and river continuum concept (RCC). Multivariate techniques were used to determine the correlation between richness and the landscape characteristics in the sampling unit, revealing that there is a greater number of species along the sites with a larger riparian zone. Some fish species have showed to be a good indicator: Hypostomus strigaticeps, Hoplosternum littorale and Salminus hilarii; on the other hand Astyanax altiparanae has not showed to be a good indicator species

Abordagens integrativas considerando diferentes dimensões da diversidade (p.ex., taxonômica, funcional, ou filogenética) cada vez mais estão sendo utilizadas para (1) avançar o nosso conhecimento sobre os mecanismos que criam e mantém a biodiversidade, e (2) elucidar a distribuição da biodiversidade tanto em áreas geográficas de interesse como dentro de áreas protegidas. De fato, entender como a biodiversidade se distribui no espaço e como ela é mantida ao longo do tempo é fundamental para embasar o planejamento de áreas protegidas e corredores ecológicos, assim como auxiliar no manejo de espécies invasoras, restauração de habitats degradados e manejo de ecossistemas. Nessa perspectiva, os objetivos centrais desta tese foram: (1) avaliar os mecanismos ecológicos e evolutivos, que potencialmente influenciam a diversidade beta taxonômica e filogenética de árvores nas florestas Atlânticas do sul do Brasil, e (2) avaliar como os componentes taxonômicos e filogenéticos se distribuem ao longo destas florestas, e como eles são representados dentro da rede regional de áreas protegidas. Para tal, utilizei modelagem de equações estruturais (capítulo 1) para testar a validade de uma rede de hipóteses ligando dados e teoria. No capítulo 1, avaliei a relação entre a diversidade beta taxonômica e filogenética, e como elas se relacionam com a riqueza de espécies, filtragem ambiental, espaço geográfico e estrutura filogenética (agrupamento filogenético). Nesse capítulo, concluí que a diversidade beta taxonômica é influenciada principalmente pelos gradientes altitudinais e climáticos, enquanto que a diversidade beta filogenética é determinada também pelo grau de agrupamento filogenético, em nível local, que provavelmente reflete o conservadorismo de nicho dentro das linhagens e distúrbio humano, que historicamente tem conduzido as florestas estudadas a um processo de homogeneização biótica. Em relação ao segundo objetivo, utilizei uma abordagem integrativa para predizer e mapear os componentes taxonômicos e filogenéticos da diversidade de árvores e, em seguida, avaliar a efetividade da rede de áreas protegidas em representar tais componentes nas florestas Atlânticas do sul Brasil. Nesse capítulo, concluí que as áreas protegidas são insuficientes para preservar adequadamente a biodiversidade de árvores nestas florestas. Sugeri que a expansão da rede em direção as áreas de alta singularidade taxonômica e filogenética, como definidas aqui, poderia aumentar, ao mesmo tempo, a representação da riqueza de espécies, da diversidade beta e da história evolutiva das espécies estudadas. Sugeri também que a inclusão de áreas de alta insubstituibilidade, em termos de história evolutiva, poderia ajudar a aumentar a proteção da diversidade de características e do potencial evolutivo das espécies. / Integrative approaches considering different dimensions of biodiversity are increasingly being used in ecology and conservation to (1) advance our knowledge about the mechanisms underlying current patterns of biological diversity, and (2) elucidate the distribution of biodiversity in geographical areas of interest, and within the protected areas. Indeed, understanding how biodiversity is distributed in space and how it is maintained over time is critical to support the planning of protected areas and ecological corridors as well as assist the management of invasive species, the restoration of degraded areas and ecosystem management. In this perspective, the central goals of this thesis were: (1) to evaluate the ecological and evolutionary mechanisms that potentially influence the tree taxonomic and phylogenetic beta diversity in Atlantic forests located in southern Brazil, and (2) to evaluate how the taxonomic and phylogenetic diversity components are distributed across these forests, and how they are represented within the regional network of protected areas. For this, I used structural equation modeling (chapter 1) to test the validity of a network of hypotheses linking data and theory. In the chapter 1, I evaluate the relationship between taxonomic and phylogenetic beta diversity, and how they are related to species richness, environmental filtering, geographical space and phylogenetic structure (phylogenetic clustering). In this chapter, I conclude that taxonomic beta diversity (at the study scale) is mainly driven by the altitudinal and climatic gradients, while phylogenetic beta diversity is also determined by the degree of phylogenetic clustering at local level, more likely reflecting niche conservatism within lineages and human disturbance that has historically conducted the studied forests to a process of biotic homogenization. In relation to the second goal, I used an integrative approach to predict and map the taxonomic and phylogenetic components of tree diversity, and to assess the effectiveness of the protected areas network in representing these components in the Atlantic forests. In this chapter, I conclude that protected areas are insufficient to adequately preserve the tree biodiversity in these forests. I suggest that expanding the network towards the areas of taxonomic and phylogenetic uniqueness, as defined here, could increase the representation of species richness, beta diversity and evolutionary history of angiosperm trees at the same time. Furthermore, the inclusion of areas of high irreplaceability in terms of evolutionary history could help to improve the protection of feature diversity and evolutionary potential of species.

O manejo de campo nativo apresenta o desafio de desenvolver estratégias de intensificação sustentável para superar o dilema produçãoconservação. Embora a intensificação da produção através da agregação de insumos (fertilizantes e/ou sementes) seja possível, também pode causar mudanças negativas na sustentabilidade. Apesar das quantificações preliminares, existe uma lacuna no conhecimento acerca de como e quando são alteradas a diversidade, a estabilidade e a resiliência em processos de intensificação. Neste sentido, esta tese se concentra em identificar, através de dois experimentos: i) os principais fatores de controle da estabilidade temporal da produtividade de pastagens enriquecidas com nitrogênio (N), fósforo (P) e água; e ii) determinar os efeitos da fertilização fosfatada na diversidade de espécies e no estado da vegetação em campos nativos sobressemeados com leguminosas exóticas. O primeiro experimento apresenta o efeito de quatro anos de adição de N, P e água na produtividade e estabilidade temporal da produção. A adição de N e N + P diminuiu a estabilidade, processo associado à redução da constância da produção das espécies mais dominantes, enquanto que as adições de P e água incrementaram a estabilidade devido ao aumento da assincronia das espécies. Estas duas formas de controle da estabilidade são alternativas e a expressão está regulada pela limitação de N. Contrariamente ao proposto na teoria predominante “diversidade-estabilidade”, os resultados deste trabalho indicam que a estabilidade da produção depende principalmente do comportamento das espécies dominantes e não da diversidade de espécies. O segundo experimento expõe o efeito de mais de 10 anos de fertilização fosfatada na diversidade de espécies de um campo nativo sobressemeado com Trifolium repens e Lotus corniculatus. As respostas em riqueza e diversidade de espécies se relacionaram negativamente com a concentração de P do solo. Foram identificados limiares de concentração de P a partir dos quais se alcançaram as perdas máximas de diversidade e também foi desenvolvido um modelo de estados e transições da vegetação. Em síntese, esta tese contribui para ampliar o conhecimento do impacto de práticas de melhoramento em atributos de sustentabilidade (produtividade, diversidade, estabilidade, e resiliência) dos pastos nativos do bioma Pampa. A continuação destes esforços permitirá avanços na definição dos limites da intensificação baseados em critérios ecológicos, e assim contribuirá com o desafio de desenvolver estratégias de manejo sustentável. / Native grassland management faces the challenge to develop sustainable intensification strategies to overcome the dilemma between production and conservation. Although the intensification of the production through addition of inputs (fertilizers and/or seeds) to be possible, it can potentially induces negative changes in the sustainability of the ecosystems. There is a gap in the knowledge about how and when diversity, stability and resilience are altered in the intensification process. The main body of this thesis consist of two experiments focused on: i) identifying the main factors that control the temporal stability of productivity of a native grassland enriched with nitrogen (N), phosphorus (P) and water; and ii) determining the effects of phosphorus fertilization in the diversity and the state of the vegetation of a native grassland overseeded with exotic legumes. The first experiment analyzed the effect of four years of N, P and water addition on the productivity and the temporal stability of a native grassland production. The single addition of N or combined with P decreased the temporal stability by reducing the constancy of the production of the most dominant species, whereas the additions of P and water increased the stability by increasing species asynchrony. Both controls of temporal stability appear to be alternative mechanisms, and the specific expression of each one would be regulated by the limitation of N. In the second experiment, the long term effects of two P fertilization doses on species richness and diversity of a native grassland overseeded with Trifolium repens and Lotus corniculatus were examinated. Extractable soil P was negatively related with species richness and diversity. Additionally, P concentration thresholds related to the maximum loss of species richness and diversity were identified, and a model of the states and transitions of the vegetation was developed. In summary, this thesis contributes to the understanding of the impact of intensification practices on sustainability attributes (productivity, diversity, stability and resilience) of native grasslands. The continuation of this research will focus on a detailed definition of the thresholds of the intensification based on ecological criteria, and thus contribute to the challenge to develop sustainable systems.

Small mammals are a keystone guild in arid ecosystems; often exhibiting top-down control of the diversity and structure of plant communities. However, changing climate, shifting fire regimes, and the invasion of exotic plants are modifying the structure of arid systems. Environmental changes in these arid systems are likely altering small mammal communities, and therefore, their ecological role. We examined two aspects of the community composition of small mammals in the Great Basin: changes in community composition since large scale sampling of the region began in 1930, and the current population of a sensitive species of small mammal, the dark kangaroo mouse (Microdipodops megacephalus). In Chapter 1, we compared diversity and composition of present day small mammal communities to communities sampled between the years of 1930 and 1980. We sampled 234 historical locations across the eastern Great Basin region during the summers of 2014 and 2015. Our results indicated that diversity, richness, and evenness of small mammals in the Great Basin have declined significantly over the last century (P=0.002, P=0.03, P=0.002). The relative abundance of generalist species has increased, while specialist species have declined (P<0.001, P<0.001). Also, community composition at each site has changed significantly over the past century. Alterations in the community structure of small mammals may have cascading implications for the future of the Great Basin ecoregion. In Chapter 2, we conducted a region-wide survey for the dark kangaroo mouse in western Utah. Four teams sampled 232 locations across western Utah during the summers of 2014-2015. Of the 232 sites sampled, only 5 sites resulted in dark kangaroo mouse captures, totaling 15 individuals. These results could indicate a state-wide population decline for this species, both compared to historic population levels and to the populations surveyed less than ten years ago. The rapid decline may be a result of habitat degradation associated with invasive plant species and increasing fire frequency, the effects of which are exacerbated by the dark kangaroo mouse's life history as an ecological specialist. Unless large-scale habitat restoration and preservation is conducted for remaining populations, it is likely the dark kangaroo mouse will continue to decline within the state.

In the tropics, widespread deforestation and conversion of primary forests to agricultural and pasture lands has resulted in losses of composition, structure, and functions of forest landscapes. Deforestation in the tropics is typically preformed via slash-and-burn practices; the byproducts from combustion have been identified as the second-highest form of anthropogenically derived 'greenhouse-gases' (such as carbon dioxide) to the atmosphere, and have been linked to the warming of the earth. Landscape-scale measures of species composition and biomass structure of primary forests are important for two reasons: (i) they provide accurate, land-based measures to predict what has been lost due to land-uses, and (ii) they aid in the discovery of key factors which explain patterns in compositional and structural diversity that are useful for defining conservation objectives. In this thesis, I enumerate the landscape-level patterns in species composition and biomass and C structure for 20-0.79 ha primary tropical forest stands within the region of "Los Tuxtlas", Veracruz, Mexico. These 20 sites were selected to capture the variability in composition and structure with respect to an array of environmental variables. These variables included a wide elevational range (15-1280 m.a.s.l.), variable slopes (Range: 3-41% slope), 3 soil-types (ash derived, lava flows, and weathered soils), a gradient of mean annual temperatures (~19.5-25.7��C), a broad precipitation range (2500 - 4000 mm year�����), a rainfall frequency range (i.e. max rainfall in 24 hours; ranged 30->100 mm day�����), and 3 Holdridge Life Zones (Tropical Moist Forest, Subtropical Wet Forest, and Subtropical Lower Montane Rain Forest). Species composition was highly correlated with the environmental variables, particularly elevation. In general for plants ���10 cm dbh, site species richness declined at a rate of ~2 species per 100 m rise in elevation. Forest sites located at similar elevations were most similar in their species compositions as compared with sites separated by large elevational differences. Despite the gradual change in species richness and composition, four sub-regions, or forest environments, within Los Tuxtlas were identified that had different species compositions and distinct combinations of elevation, soil-types, and climates. These four sub-regions were described as community-types according to their geographic location: Lowland-Reserve (LR), La Perla Plateau (LP), Volcanic Upslope (VU), and Cloud Forests (CF). The LR, LP, and VU community-types were coarsely described as Tropical Evergreen Forests (TEF's; INEGI 2001). All community-types corresponded with classifications within the Holdridge Life Zone System; the LR community-type was classified as Tropical (transition to Subtropical) Moist Forest; LP and VU community-types were classified as Subtropical Wet Forest, and the Cloud Forest community-type was classified as Subtropical Lower Montane Rain Forest. These community-types and Life Zones are useful tools for conservation, as they represent unique forests that collectively capture much of the variation in the species richness and compositional diversity of the Los Tuxtlas region. Unlike species composition, the variability in forest structure among the 18 TEF sites was not associated with the environmental variables of the Los Tuxtlas landscape. On average, TEF's had a total aboveground biomass (TAGB) of 422 �� 17 Mg ha����� and 205 �� 8 Mg ha����� total aboveground carbon (C). The TAGB and C pools for Cloud Forests was ~18% lower than TEF's, and averaged 346 �� 1 and 168 �� 1 Mg ha�����, respectively. The majority of this biomass difference was due to large trees within the forest structure. Cloud Forests had generally fewer trees ���70 cm dbh, and a more even distribution of trees 30-70 cm dbh than TEF's. The biomass contribution of large trees (���70 cm dbh) accounted for most, if not all, of the variation in TAGB and C for these tropical forests. The relatively high TAGB and C pools implicates Los Tuxtlas forests as a significant pool of aboveground biomass and C within the Neotropics. / Graduation date: 2002

Fragmentation of the Atlantic forest is extensive and a major reason for biodiversity loss in the South American continent. Today only a fraction of the pre-Colombian forest cover is still left and predominantly represented by isolated fragments. In the highlands of southern Brazil the biome constitutes the eco-region Araucaria moist forest that has a unique plant composition and many endemic species. This study has focused on one small fragment of Araucaria moist forest within the state Rio Grande do Sul in southern Brazil. The study was performed as an inventory of the tree species present in the fragment to acknowledge its diversity and tree species composition. From this the origin and conservation status for the fragment could be concluded. The inventory demonstrated high species diversity for the fragment with a Shannon index of nearly 3,43. Also many similarities to natural Araucaria moist forest were evident with the occurrence of 12 of the 19 native species most represented in natural forests. A high percentage of dead trees were documented with nearly 6,5 % . Further the endemic species Dicksonia sellowiana and Nectandra megapotamica were recorded within the fragment, D. sellowiana is an endangered species in Brazil. These results indicated a fragment with natural origin as part of the mosaic composition in the eco-region rather than a result of human land use such as plantation or regrowth of agricultural land. Thus the fragment may be a remnant from the great Araucaria forest expansion occurring in the second part of the Late Holocene with an age of up to 1100 years. This study suggests that the surveyed Araucaria moist forest fragment has significant conservation status and deserves accurate conservation measures to be taken for the continuing existence of this unique and threatened eco-region.