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No. of bitstreams: 2 license_rdf: 23148 bytes, checksum: 9da0b6dfac957114c6a7714714b86306 (MD5) José Neiva Mesquita Neto.pdf: 2799737 bytes, checksum: 590e98d41066ac6babc47eeb04637796 (MD5) Previous issue date: 2013-09-19 / Conselho Nacional de Pesquisa e Desenvolvimento Científico e Tecnológico - CNPq / Coordenação de Aperfeiçoamento de Pessoal de Nível Superior - CAPES / Plant-pollinator interactions in syncronopatric species of Psychotria (Rubiaceae). Psychotria species are commonly found in the understory of forested areas in tropical regions, and are important components for the functioning of these ecosystems. Many species of the genus are sympatric and bloom during the same period, being considered potentially syncronopatrics. For this reason, this genus has been considered as a good model to infer general patterns and mechanisms of speciation in the tropics. In the first paper of this dissertation, the interactions between potentially sympatric species of Psychotria and their pollinators were analyzed in order to verify the possible existence of sharing, specialization or generalization of pollinators and plants in the analyzed system. Then, data of secondary studies that contained identifying pollinators of Psychotria were analyzed From these data, we generated graphs and analyzes of interaction networks and niche overlap. Altogether, nine species of Psychotria and 25 species of pollinators of occurrence in the Atlantic Forest were included in the analyzes. The plant with the most generalist network is Psychotria tenuinervis and the pollinators with the highest proportion of links and consequently with more important role in the network belonged orders Lepidoptera and Hymenoptera. Psychotria species showed niche overlap in pollination and pollinator sharing. The period of greatest intensity of flowering coincided with the rainy season in the Atlantic Forest, with up to seven species coflowering. Because Psychotria species occur in sympatry and have flowering overlap and asymmetric interactions with flower visitors, it is possible that they are involved in a process of facilitation in pollination. The second paper aimed to investigate if four sympatric populations of Psychotria show pollinators sharing and pollination niche overlap . Another objective was to determine if their flowering season are synchronics. We found a dual synchrony in this system, the first in the intensity of flowering among the populations of Psychotria and the second in the increase of the abundance of flowers and pollinators. The species of Psychotria showed sharing fundamental niche of pollination and positive impact on reproductive success. However, we note that the sharing of pollinators can not be generalized to the entire system, but to the modules or pairs of species. Thus, each species of Psychotria has one or more species of preferential pollinator for sharing and that this relationship is not always reciprocal. This reinforces that the interactions among the plant species are asymmetric. / Interação planta-polinizador em espécies sincronopátricas de Psychotria (Rubiaceae). Psychotria contribui de forma importante para a diversidade florística tropical e são comumente encontradas em sub-bosque de áreas florestadas em regiões tropicais, sendo importantes componentes para o funcionamento destes ecossistemas. Muitas espécies do gênero são simpátricas e florescem em um mesmo período do ano, sendo consideradas potencialmente sincronopátricas. Por esta razão, este gênero tem sido considerado como um bom modelo para inferir padrões e mecanismos gerais de especiação nos trópicos. No primeiro artigo, as interações entre espécies potencialmente simpátricas de Psychotria e seus polinizadores foram analisadas com o objetivo de verificar a possível existência de partilha, de especialização ou generalização de polinizadores e plantas no sistema analisado. Para isso, foram incluídas informações secundárias de estudos que continham a identificação em nível de espécie de polinizadores de Psychotria. A partir desses dados, foram gerados grafos e realizadas análises de redes de interação e sobreposição de nicho. Ao todo, foram incluídas nas análises nove espécies de Psychotria com registro de ocorrência para a Mata Atlântica, sendo que elas interagiram com 25 espécies de polinizadores. A planta mais generalista da rede foi Psychotria tenuinervis e os polinizadores que concentraram maior número de links e consequentemente com papel mais importante na rede pertenceram as ordens Lepidoptera e Hymenoptera. As espécies de Psychotria apresentaram sobreposição de nicho na polinização com partilha de polinizadores. O período de maior intensidade de floração coincidiu com o período chuvoso na Mata Atlântica, com até sete espécies apresentando coflorescimento. Assim, pode-se inferir que a polinização em Psychotria demanda polinizadores generalistas. Pelo fato das espécies de Psychotria ocorrerem em simpatria, possuírem floração sobreposta e interações assimétricas com visitantes florais, é possível que estejam envolvidas em um processo de facilitação na polinização. Já o segundo artigo objetivou averiguar se quatro populações simpátricas de Psychotria, em cofloração, apresentaram partilha de polinizadores e sobreposição de nicho na polinização. Além disso, objetivou verificar se existe sincronia entre as populações vegetais e destas com comunidade de polinizadores. Foi encontrada uma dupla sincronia nesse sistema, sendo a primeira na intensidade de floração entres as populações de Psychotria e a segunda no aumento da abundância de flores e de polinizadores. As espécies de Psychotria apresentaram partilha fundamental do nicho da polinização e com reflexo positivo no sucesso reprodutivo. No entanto, verificamos que a partilha de polinizadores não pode ser generalizada a todo o sistema, mas sim a módulos ou pares de espécies. Dessa forma, cada espécie de Psychotria possui uma ou mais espécies preferencias para partilha de polinizadores e que nem sempre essa relação é reciproca. Isso reforça que as interações entre as plantas são assimétricas.

Deforestation of the Brazilian savanna (Cerrado) region has caused major changes in hydrological processes. These changes in water balance and soil erosion are still poorly understood, but are important for making land management decisions in this region. Therefore, it is necessary to understand the magnitudes of hydrological processes and soil erosion changes on local, regional and continental scales, and the consequences that are generated. The main objective of the study presented in this doctoral thesis was to better understand the mechanism of hydrological processes and soil erosion in the Cerrado. To achieve that, I worked with different scales (hillslope, watershed and continental) and using data from experimental field, laboratory, and remote sensing. The literature review reveals that the annual rainfall erosivity in Brazil ranges from 1672 to 22,452 MJ mm ha-1 h-1 yr-1. The smallest values are found in the northeastern region, and the largest in the north and the southeastern region. I found that the canopy interception may range from 4 to 20% of gross precipitation and stemflow around 1% of gross precipitation in the cerrado. The average runoff coefficient was less than 1% in the plots under cerrado and that the deforestation has the potential to increase up to 20 fold the runoff coefficient value. The results indicate that the Curve Number method was not suitable to estimate runoff under undisturbed Cerrado, bare soil (hydrologic soil group A), pasture, and millet. Therefore, in these cases the curve number is inappropriate and the runoff is more aptly modeled by the equation Q = CP, where C is the runoff coefficient. The water balance from the remote sensing data across the Brazilian Cerrado indicates that the main source of uncertainty in the estimated runoff arises from errors in the TRMM precipitation data. The water storage change computed as a residual of the water budget equation using remote sensing data (TRMM and MOD16) and measured discharge data shows a significant correlation with terrestrial water storage change obtained from the GRACE data. The results show that the GRACE data may provide a satisfactory representation of water storage change for large areas in the Cerrado. The average annual soil loss in the plots under bare soil and cerrado were 15.25 t ha-1 yr-1 and 0.17 t ha-1 yr-1, respectively. The Universal Soil Loss Equation cover and management factor (C-factor) for the plots under native cerrado vegetation was 0.013. The results showed that the surface runoff, soil erosion and C-factor for the undisturbed Cerrado changes between seasons. The greatest C-factor values were found in the summer and fall. The results found in this doctoral thesis provide benchmark values of the water balance components and soil erosion in the Brazilian Cerrado that will be useful to evaluate past and future land cover and land use changes for this region. In addition, I conclude that the remote sensing data are useful to evaluate the water balance components over Cerrado regions, identify dry periods, and assess changes in water balance due to land cover and land use change. / O desmatamento nas regiões de Cerrado tem causado intensas mudanças nos processos hidrológicos. Essas mudanças no balanço hídrico e erosão do solo são ainda pouco entendidas, apesar de fundamentais na tomada de decisão de uso e manejo do solo nesta região. Portanto, torna-se necessário compreender a magnitude das mudanças nos processos hidrológicos e de erosão do solo, em escalas locais, regionais e continentais, e as consequências dessas mudanças. O principal objetivo do estudo apresentado nesta tese de doutorado foi de melhor entender os mecanismos dos processos hidrológicos e de erosão do solo no Cerrado Brasileiro. Para tanto, utilizou-se diferentes escalas de trabalho (vertentes, bacias hidrográficas e continental) e usando dados experimentais in situ, de laboratório e a partir de sensoriamento remoto. O estudo de revisão de literatura indica que a erosividade da chuva no Brasil varia de 1672 to 22,452 MJ mm ha-1 h-1 yr-1. Os menores valores encontram-se na região nordeste e os maiores nas regiões norte e sudeste do Brasil. Verificou-se que os valores de interceptação da chuva variam de 4 a 20% e o escoamento pelo tronco aproximadamente 1% da precipital total no cerrado. O coeficiente de escoamento superficial foi menor que 1% nas parcelas de cerrado e o desmatamento tem o potencial de aumentar em até 20 vezes esse valor. Os resultados indicam que o método Curve Number não foi adequado para estimar o escoamento superficial nas áreas de cerrado, solo exposto (grupo hidrológico do solo A), pastagem e milheto. Portanto, nesses casos o uso do CN é inadequado e o escoamento superficial é melhor estimado a partir da equação Q = CP, onde C é o coeficiente de escoamento superficial. O balanço hídrico a partir de dados de sensoriamento remoto para todo o Cerrado Brasileiro indica que a principal fonte de incerteza na estimativa do escoamento superficial ocorre nos dados de precipitação do TRMM. A variação de água na superfície terrestre calculada como o residual da equação do balanço hídrico usando dados de sensoriamento remoto (TRMM e MOD16) e valores observados de vazão mostram uma correlação significativa com os valores de variação de água na superfície terrestre provenientes dos dados do GRACE. Os dados do GRACE podem representar satisfatoriamente a variação de água na superfície terrestre para extensas regiões do Cerrado. A média anual de perda de solo nas parcelas de solo exposto e cerrado foram de 15.25 t ha-1 yr-1 and 0.17 t ha-1 yr-1, respectivamente. O fator uso e manejo do solo (fator C) da Universal Soil Loss Equation para o cerrado foi de 0.013. Os resultados mostraram que o escoamento superficial, erosão do solo e o fator C na área de cerrado variam de acordo com as estações. Os maiores valores do fator C foram encontrados no verão e outono. Os resultados encontrados nesta tese de doutorado fornecem valores de referência sobre os componentes do balanço hídrico e erosão do solo no Cerrado, que podem ser úteis para avaliar o uso e cobertura do solo atual e futuro. Além disso, conclui-se que os dados de sensoriamento remoto apresentam resultados satisfatórios para avaliar os componentes do balanço hídrico no Cerrado, identificar os períodos de seca e avaliar as alterações no balanço hídrico devido à mudanças de uso e cobertura do solo.

Die Brasilianische Savanne, auch bekannt als der Cerrado, bedeckt ca. 24% der Landoberfläche Brasiliens. Der Cerrado ist von einer einzigartigen Biodiversität und einem starken Gradienten in der Vegetationsstruktur gekennzeichnet. Großflächige Landnutzungsveränderungen haben dazu geführt, dass annähernd die Hälfte der Cerrado in bewirtschaftetes Land umgewandelt wurde. Die Kartierung ökologischer Prozesse ist nützlich, um naturschutzpolitische Entscheidungen auf räumlich explizite Informationen zu stützen, sowie um das Verständnis der Ökosystemdynamik zu verbessern. Neue Erdbeobachtungssensoren, frei verfügbare Daten, sowie Fortschritte in der Datenverarbeitung ermöglichen erstmalig die großflächige Erfassung saisonaler Vegetationsdynamiken mit hohem räumlichen Detail. In dieser Arbeit wird der Mehrwert von Landsat-basierten Landoberflächenphänologischen (LSP) Metriken, für die Charakterisierung der Cerrado-Vegetation, hinsichtlich ihrer strukturellen und phänologischen Diversität, sowie zur Schätzung des oberirdischen Kohlenstoffgehaltes (AGC), analysiert. Die Ergebnisse zeigen, dass LSP-Metriken die saisonale Vegetatiosdynamik erfassen und für die Kartierung von Vegetationsphysiognomien nützlich sind, wobei hier die Grenzen der Einteilung von Vegetationsgradienten in diskrete Klassen erreicht wurden. Basierend auf Ähnlichkeiten in LSP wurden LSP Archetypen definiert, welche die Erfassung und Darstellung der phänologischen Diversität im gesamten Cerrado ermöglichten und somit zur Optimierung aktueller Kartierungskonzepte beitragen können. LSP-Metriken ermöglichten die räumlich explizite Quantifizierung von AGC in drei Untersuchungsgebieten und sollten bei zukünftigen Kohlenstoffschätzungen berücksichtigt werden. Die Erkenntnisse dieser Dissertation zeigen die Vorteile und Nutzungsmöglichkeiten von LSP Metriken im Bereich der Ökosystemüberwachung und haben demnach direkte Implikationen für die Entwicklung und Bewertung nachhaltiger Landnutzungsstrategien. / The Brazilian savanna, known as the Cerrado, covers around 24% of Brazil. It is characterized by a unique biodiversity and a strong gradient in vegetation structure. Land-use changes have led to almost half of the Cerrado being converted into cultivated land. The mapping of ecological processes is, therefore, an important prerequisite for supporting nature conservation policies based on spatially explicit information and for deepening our understanding of ecosystem dynamics. New sensors, freely available data, and advances in data processing allow the analysis of large data sets and thus for the first time to capture seasonal vegetation dynamics over large extents with a high spatial detail. This thesis aimed to analyze the benefits of Landsat based land surface phenological (LSP) metrics, for the characterization of Cerrado vegetation, regarding its structural and phenological diversity, and to assess their relation to above ground carbon. The results revealed that LSP metrics enable to capture the seasonal dynamics of photosynthetically active vegetation and are beneficial for the mapping of vegetation physiognomies. However, the results also revealed limitations of hard classification approaches for mapping vegetation gradients in complex ecosystems. Based on similarities in LSP metrics, which were for the first time derived for the whole extent of the Cerrado, LSP archetypes were proposed, which revealed the spatial patterns of LSP diversity at a 30 m spatial resolution and offer potential to enhance current mapping concepts. Further, LSP metrics facilitated the spatially explicit quantification of AGC in three study areas in the central Cerrado and should thus be considered as a valuable variable for future carbon estimations. Overall, the insights highlight that Landsat based LSP metrics are beneficial for ecosystem monitoring approaches, which are crucial to design sustainable land management strategies that maintain key ecosystem functions and services.

Browse selection, intake, utilisation, palatability, quality and production are tightly linked and need to be considered together in trying to improve our understanding of browsing dynamics and the interactions between browsers and vegetation. Such an understanding is necessary in order to re-evaluate determinations of browser carrying capacities and evaluating actual and potential impacts of browsing animals on vegetation composition and diversity. Browser carrying capacity is determined by both the quantity and the nutritive value of forage. The measurement of browse quantity and nutritive value and the matching of browse supply to browser demand are central to sustainable utilisation and the monitoring of vegetation health. South African savannas are poorly studied with respect to tree canopy growth and browse production making it difficult to quantify the available browse biomass on which browsing capacity estimations are based, and consequently difficult to estimate levels of browsing that are sustainable. This study addressed these issues by investigating browse dynamics, broadly aiming to (1) explore factors affecting browse production, biomass and nutritive value; (2) develop models to assess and monitor these parameters across seasons and properties; (3) use the resultant models in improving our understanding of how to determine browser carrying capacities. More specifically, our study sought to examine the effects of plant physiognomy, forage nutritive value, canopy stratum, defoliation, temperature, rainfall and soil nutrient status on the browse production of evergreen (Carissa bispinosa, Euclea divinorum, Gymnosporia senegalensis), semi-deciduous (Spirostachys africana, Ziziphus mucronata) and deciduous (Acacia nilotica, Dichrostachys cinerea) savanna tree species from June 2003 – June 2005 in three sites along the northern Zululand coastline of KwaZulu-Natal. Available browse biomass, during the dry season, of four key savanna tree species (A. nilotica, E. divinorum, G. senegalensis, and S. africana) was estimated through the development of allometric regression equations. Non-linear regression was used to investigate the relation between the leaf dry mass (LDM) and canopy volume (CVol) of each of the four tree species. Exponential regression (y = a + brlnx) of the natural logarithm of CVol data provided the most accurate and precise description of the tree CVol – LDM relation. A study was undertaken to determine which factors may influence browse production in a southern African savanna. Regression tree models for the browse production identified that the dominant factors influencing browse production were CVol (m3), season, species and height to the lowest leaves of the tree canopy (HL) (m). The length of the growing season had a marked effect on the production potential of savanna tree species, suggesting that improved conditions for growth, i.e. greater rainfall, soil moisture content and improved soil nutrient availability result in a longer period of rapid sustained growth. Species was identified as an important contributing factor to differences in browse production rates, suggesting the need for the development of species or species group models. Mean annual browse production of evergreen trees was greater than that of deciduous and semi-deciduous trees. Mean quarterly (three monthly) browse production was highest, for all trees, during the wet season, with the greatest difference between wet and dry season production being observed in deciduous forms. Evergreen forms showed continuous growth over the whole study, with enhanced growth over the wet season. Deciduous forms, on the other hand, concentrated growth in spurts, when environmental conditions became favourable, with most production occurring during a short growing season. Browse nutritive value was found to be greatest during the wet season, when growth and photosynthesis are at their greatest. Further, browse nutritive value was greatest in deciduous species. Evergreen trees were found to have greater acid detergent fibre (ADF) concentrations than both the deciduous and semi-deciduous trees. By contrast, crude protein (CP) concentrations were greater in semi-deciduous and deciduous species than in evergreen species. The daily CP requirements for maintenance for an adult impala (45 kg) were met by all species over all three study areas and all seasons. Daily CP requirements for growth and lactation, however, were only ever met by deciduous and semi-deciduous species, though this result was not consistent over study areas and seasons. Predictive models for the production of browse on deciduous, semi-deciduous and evergreen trees in northern Zululand were developed using multivariate adaptive regression spline functions. The best predictors of growing season browse production in all three tree guilds (defined here as a group of trees having a characteristic mode of living) were primarily measurable tree dimensions, while the prevailing environmental conditions had little impact. Differences in the production, nutritive value and available browse biomass between the different tree forms and seasons have a profound effect on the determination of browser carrying capacities and need to be incorporated into any game or conservation management plan. / Thesis (Ph.D.)-University of KwaZulu-Natal, Pietermaritzburg, 2012.

The effects of fire and mechanical clearing were investigated for their potential in assisting with the eradication of Chromolaena odorata (previously Eupatorium odoratum). The study was divided into two focus areas, the first focused on mechanical clearing of dense stands of C. odorata on three sites and the second focused on the long term influences of a single burn on C. odorata plants in the different size categories. For mechanical clearing, two key issues were investigated; namely whether this type of clearing procedure was effective in dense C. odorata stands and whether rehabilitation was necessary in these cleared areas. The study was conducted from July 2002 to June 2004. The area was subject to a severe drought throughout the duration of the study. The severe drought had a large influence on the result in both focus areas. A bulldozer was found to be a very effective at clearing dense C. odorata stands. Results from the mechanical clearing study showed that there was still a large viable grass seed population in the areas that had been covered by a dense stand of C. odorata plants for over three years. Thus, indigenous plants were able to re-colonize the area after removal of C. odorata without human intervention, even thought the area was experiencing a severe drought. The density of C. odorata seedlings emerging in the cleared areas was far lower than expected. The C. odorata density in the permanent plots, for seedlings that germinated in the first season after clearing (SeptemberOctober 2002), was only 0.25,0.03 and 0.72 per 5 m2 in the three sites respectively by the end of the study in June 2004. For the C. odorata seedlings that germinated in the second season (September-October 2003) the density was, 0.5, 0.56 and 1.06 per 5 m2 in the three sites respectively by the end of the study in June 2004. It was suspected that the drought influenced seed germination. Unfortunately the number of C. odorata seedlings was so low, that no significant relationship could be found between grass and C. odorata seedling density. By the end of the study the grass fuel mass in all the rehabilitated sites was already over 3000 kg ha-1, even though the area was experiencing a severe drought. This grass fuel load, when burnt, will assist land managers in controlling C. odorata plants, especially seedlings. Very few other alien invasive plant species emerged in the cleared areas. At the Mhlosinga site, Senna pendula made up less than one percent of the herbaceous species composition and only a single Ricinus communis plant was recorded. No alien plant species were recorded on the other two sites. Results from the burning trials revealed that plants in all the size categories were affected by fire. Greater fuel masses and fire intensities were required to kill larger C. odorata plants relative to smaller ones. Fire was found to be very effective at eliminating small and medium size C. odorata plants. Fire applied as a once off treatment had a significant long-term effect on the C. odorata population. The following fuel loads were required to achieve 80% mortality in this 11 study: for small plants a fuel load of over 4000 kg ha-I, for medium plants a fuel load over 4200 kg ha-I and for large plants a fuel load over 4600 kg ha-I. Little difference could be detected between a head or a back burn, as both fire types had their own advantages and disadvantages. Although some of the C. odorata plants in the burnt plots had not perished by the time of the first investigation, following the burn (February 2003), by the time of the second investigation (June 2004), many of these plants had eventually succumbed. These results highlighted the fact that plants which are damaged by fire were more likely to persish during an extended droughts period, than plants which were not subjected to fire. Results from the control plots, in the burning trials, for medium and large plants showed dramatic increases in density over time. Tagged individuals from the control plots did reveal that some of the medium and large plants did die during the drought, although the amount was negligible when compared to the number of new plants growing into the new size categories. A large proportion of the small plants in the control plots also survived the drought with many of them even growing into the medium category. The difference between the control plots and the burnt plots was obvious and significant, especially once the fuel mass exceeded 3783 kg ha-I. Results from this study show that fire can be used as a very effective tool in assisting land managers to control C. odorata in open savanna bushveld. / Thesis (M.Sc.)-University of KwaZulu-Natal, Pietermaritzburg, 2006.

The savanna woodlands of Southern Africa, colloquially termed the miombo, are poorly described in terms of biodiversity compared to other biomes. They have therefore been underrepresented in the wider understanding of how land use intensification is shaping global biodiversity. Land use change is known to reduce biodiversity and disrupt intactness of ecological communities with consequences for ecosystem functioning, resilience, and services. Miombo woodlands are described as biodiversity hotspots due to a high endemism of species and the presence of megafauna. At the same time, they are also considered dynamic socio-ecological systems shaped by disturbances and the land use activities of people. The patterns of biodiversity change in these tropical ecosystems may, therefore, have their own unique contexts, understanding of which will be essential for biodiversity and land use management in these ecosystems. In this thesis, I identified the patterns of biodiversity change in response to the two major land use practices in the two dominant woodland types in southern African woodlands: the selective logging due to charcoal production in the mopane woodlands, and agricultural expansion in the miombo. I also examined the impact of two main disturbance agents, humans and elephants, on habitat structure and biodiversity in mopane woodlands. Across all chapters in this thesis, I investigated the effects of land use change and habitat modification on biodiversity empirically using chronosequences. To understand biodiversity change, I employed a hierarchical multilevel modelling approach making inferences at the three levels of ecological communities: species, community, and meta-community (set of ecological communities at different sites). I selected six villages in the charcoal production hotspot of southern Mozambique and carried out field surveys for three taxonomic groups: trees, mammals and ground beetles. I modelled the counts of trees and beetles and incidence of mammals using meta-community occurrence models in a Bayesian framework with the intensity class of the villages, above-ground biomass and land cover type as predictors. The results suggested that the species richness of trees and mammals declined by 12 and 8.5 % respectively while that of beetles increased by 3.5%, albeit non-significantly. In addition, the beta diversity of trees decreased while that of mammals increased. The results show that while both trees and mammals reduced in richness, they responded differently to charcoal production in terms of community organisation. The trees underwent subtractive homogenisation (decrease in alpha and beta diversities) primarily because of deterministic processes induced by selective harvesting of tree stems for charcoal. Mammal communities, on the other hand, showed subtractive heterogenization (decrease in alpha, but increase in beta diversity) mainly due to random extinctions. In the agriculture frontier of miombo-dominated northern Mozambique, I investigated the effects of fragmentation and habitat loss caused by agricultural expansion on diversity and composition of trees and mammals. I modelled the occurrences of trees and mammals using occupancy models with the fragmentation and quantity of woodland cover as predictors. The model showed that most tree species (n=10), mainly the timber and firewood species, linearly declined in population size as fragmentation increased. Mammals, on the other hand, showed a nonlinear response. Seven mammal species increased at the lower levels of fragmentation. However, at the higher levels, none of the mammal species increased while two declined. Similarly, the species richness of trees linearly declined, while that of mammals increased up to a fragmentation level of 55-65% and declined above this limit. The beta diversity of trees increased with fragmentation while that of mammals decreased. The results suggest that, although fragmentation reduces species richness of both trees and mammals, it affects their species compositions in different ways. Trees undergo subtractive heterogenization due to random species losses while mammals experience subtractive homogenisation mainly due to the combined effects of fragmentation-led habitat loss and intensified hunting. Finally, this study concludes that, above 75% fragmentation or below 26% habitat quantity, both taxonomic groups endure biodiversity loss. The threshold results here corroborate similar habitat quantity thresholds (20-30%) observed elsewhere in different ecosystems. However, they differ with the widespread notion that above 30% habitat quantity, the effect of fragmentation is non-existent. The results here emphasize that taxonomic groups respond differently, the diversity and population size of mammals reduced only after the habitat threshold, whereas, those of trees showed linear decrease with fragmentation most likely due to fragmentation-led habitat loss. Lastly, I examined the effects of disturbance by humans and elephants on habitat structure and bird diversity by conducting a space for time substitution comparison in the mopane woodlands of Zambia. To examine the woodland structure, I modelled the structural attributes of habitat (stem diameter, stand density, and basal area) using mixed models with the proportion of affected stems by humans and elephants as explanatory variables. I found that elephant disturbance was associated with higher stem diameters, low stand densities, but no change in basal area. Human disturbance, on the other hand, was related to reductions in stand density and basal area, but no change in the stem diameter. Further, I tested species and functional diversity of birds against the covariates of habitat structure and disturbance. I found that bird communities reduced in species richness in both, human as well as elephant disturbed areas. However, the functional diversity did not change with elephant disturbance. I concluded that human disturbance reduces woody biomass (basal area is correlated with woody biomass) of mopane woodlands and functional diversity of birds whilst elephants do not. In this thesis, I conclude that human driven land use change in the miombo woodlands erodes alpha diversity of all taxonomic groups. However, increases in beta diversity of mammals with charcoal land use and trees in agricultural land use may maintain their diversities at the meta-community level.

Made available in DSpace on 2016-06-02T19:29:57Z (GMT). No. of bitstreams: 1 5249.pdf: 4090294 bytes, checksum: 3e43d0f22c6895a3bc1866edf5eafc88 (MD5) Previous issue date: 2012-06-29 / Financiadora de Estudos e Projetos / Nesting is a critical step on bird s life cycle, since nest predation is high all over the world. Predation influences the population dynamics, the community structure and the life history of birds. Birds evolved anti-predatory strategies, which include selection of safer places for nesting. Here we intent to: (i) analyze habitat characteristics selected by adults, and (ii) evaluate the influence of these elements on nests success, and fitness consequences to individuals. We studied the Lesser Elaenia (Elaenia chiriquensis), a migratory bird that breeds in Brazilian Savannas. We conducted the study between 2010 e 2011 in a 100 ha area in the Estação Ecológica de Itirapina, a protected area in São Paulo state, were the Lesser Elaenia is abundant along its breeding season (September to December). We analyzed habitat selection comparing characteristics of used and available patches. We made all tests using chi-square tests, analysis of variance, paired t-tests and permutation tests. We used program MARK to evaluate the influence of all of the parameters on nests success. We created a set of models that included temporal and a set of environmental parameters and used Akaike s Information Criterion to evaluate the adjustment of each model to our data. Adults apparently selected anemochoric plants, with larger crowns and more lichen flakes on stalks, but did not show preference for specific plant species. Individuals also preferred patches with high plant density and high density of Aspidosperma tomentosum, the most used plant as nest substrate. Contrary of our expectations, none of these characteristics influenced nests success. However, some parameters not evaluated for selection, influenced the offspring survival. Vegetation density on nest sites was the most important variable, probably because it helps concealing nests and parental activities. Nest age and time along the breeding season were also important elements and both reduced nests success. Nest predation, habitat selection, and their consequences to the fitness are complex and are related to many variables. The present study contributed with the knowledge on this subject in tropical areas. / A nidificação é uma etapa crítica no ciclo de vida das aves, uma vez que a predação de ninhos é alta em todo o globo. Ela exerce influência na dinâmica das populações, estrutura das comunidades e evolução da história de vida do grupo. Diante disso, evoluíram estratégias antipredação, entre elas, a seleção de hábitats seguros para a nidificação pelos adultos. Assim, nesse trabalho tivemos como objetivos principais (i) conhecer os elementos do hábitat de nidificação selecionados pelos adultos e (ii) avaliar a influência desses elementos no sucesso dos ninhos, de forma a conhecer o valor adaptativo das escolhas dos adultos. Trabalhamos com Elaenia chiriquensis, um Passeriforme migratório que nidifica em áreas de Cerrado no Brasil. Conduzimos o estudo entre 2010 e 2011, em uma área de 100 ha na Estação Ecológica de Itirapina, unidade de conservação localizada no interior paulista, em que E. chiriquensis é abundante na estação reprodutiva (setembro a dezembro). Fizemos as análises de seleção do hábitat de nidificação comparando características das manchas de nidificação às manchas nas imediações, disponíveis aos casais. Usamos testes de Qui- Quadrado, análises de variância (ANOVAs), testes de permutação e testes-t pareados para as variáveis amostradas. Para avaliarmos a influência dessas e de outras características, relacionadas aos ninhos, na sobrevivência da prole, usamos o programa MARK. Criamos modelos que incluíam variáveis temporais e nossas variáveis de interesse e avaliamos, usando o critério de informação de Akaike, o ajuste dos modelos ao nosso conjunto de dados. Os adultos aparentemente selecionaram vegetais anemocóricos, com copa de tamanho maior e maior abundância de liquens nos caules como substrato dos ninhos, mas não exibiram preferência pelas espécies usadas como substrato. Elaenia chiriquensis também mostrou preferência por locais com alta densidade de vegetação lenhosa e alta abundância de Aspidosperma tomentosum, a espécie vegetal mais usada como substrato dos ninhos. Contrariando nossas expectativas, nenhuma dessas características teve influência no sucesso dos ninhos. No entanto, características relacionadas aos ninhos, e que não foram avaliadas quanto à seleção, tiveram influência na sobrevivência da prole. A mais importante delas foi a densidade de vegetação nos sítios de nidificação, que provavelmente reduz as chances de encontros com predadores e oculta a atividade dos adultos. A idade dos ninhos e a influência do tempo ao longo das estações também foram variáveis de peso na explicação dos dados e ambos reduziram as chances de sucesso dos ninhos. A predação de ninhos, a seleção do hábitat de nidificação e as consequências para o fitness dos indivíduos são assuntos de grande complexidade biológica e envolvem diversas variáveis. O presente estudo contribui com o conhecimento acerca do assunto em áreas tropicais.

Com base em um estudo interdisciplinar, os objetivos deste trabalho foram: estudar a dinâmica da vegetação e do nível relativo marinho e inferir o clima, durante o Holoceno, na região nordeste do estado do Espírito Santo. Para tanto foram analisados: (i) vegetação atual (caracterização botânica e \'delta\'13C e \'delta\'15N); (ii) matéria-orgânica do solo (\'delta\'13C, C elementar e datação 14C); (iii) sedimento lacustre (litologia, C e N elementar, \'delta\'13C e \'delta\'15N, datação 14C da matéria-orgânica, pólen e diatomáceas). Os pontos de amostragem estão localizados na Reserva Natural Vale e na Reserva Biológica de Sooretama, região de predomínio de Floresta Ombrófila Densa das Terras Baixas, com fragmentos de Savana e áreas ocupadas por vegetação pioneira. As principais conclusões foram: (i) o local de estudo não apresentou retração florestal durante o Holoceno; (ii) o clima foi inferido como predominantemente úmido; (iii) a dinâmica da vegetação durante o Holoceno no interior e nas proximidades do vale do Rio Barra Seca foi influenciada pelas flutuações do nível relativo marinho: com a transgressão marinha (há aproximadamente 7700 anos cal. A.P.) iniciou-se o deslocamento da vegetação florestal e a instalação do manguezal; entre aproximadamente 4700 até 3000 anos cal. A.P., o período de maior influência marinha, ocorreu o maior distanciamento do manguezal em relação ao ponto estudado; com a regressão marinha, a colonização do vale por vegetação pioneira ocorreu a partir de, aproximadamente, 2300 anos cal. A.P.; há cerca de 1200 anos cal. A.P. ocorreu a instalação do atual ambiente lacustre com a floresta em seu entorno; (iv) o local atualmente ocupado pela Lagoa do Macuco, no interior do vale do Rio Barra Seca, foi caracterizado por um ambiente estuarino durante o período aproximado de 7700 a 3000 anos cal. A.P / Based on an interdisciplinary study, the objectives of the present work were to study the vegetation and relative sea-level dynamics and to infer the climate during the Holocene, at northeastern region of Espírito Santo State. The materials and respective analyses were: (i) modern vegetation (botanic identification, \'delta\'13C and \'delta\'15N); (ii) soil organic matter (total organic carbon, \'delta\'13C and 14C dating); (iii) lake sediment (lithology, total organic carbon and total nitrogen, \'delta\'13C and \'delta\'15N, 14C dating, pollen and diatoms). The sampling points were located at Vale Natural Reserve and Sooretama Biologic Reserve, region of tropical rainforest vegetation dominance, with savanna fragments and pioneer vegetation patches. The main conclusions were: (i) the forest retreatment was not observed in the study site during the Holocene (ii) the climate was predominantly humid (iii) vegetation dynamics inside the Barra Seca River valley and surroundings were influenced by relative sea-level fluctuations: at ca. 7700 cal. yr B.P., the forest vegetation started its retreatment and the mangrove ecosystem was installed; from ca. 4700 to ca. 3000 cal. yr B.P., the period of higher marine influence, occurred the higher mangrove detachment from the sampling point; with the marine regression, the valley colonization by the pioneer vegetation started at ca. 2300 cal. yr B.P.; at ca. 1200 cal. yr B.P. started the installation of modern lacustrine environment, with the Forest in the surroundings; (iv) the present location of Lagoa do Macuco was characterized by na estuarine environment during the period from ~7700 to ca. 3000 cal. yr B.P

Em diversos estudos ao redor do globo, a estrutura e heterogeneidade da vegetação têm se mostrado um fator determinante na diversidade de espécies de aves e também de outros grupos de animais. O Cerrado é o segundo mais extenso e mais ameaçado bioma de ocorrência no Brasil. Este bioma também é caracterizado por um evidente gradiente ambiental de estrutura e heterogeneidade de vegetação. Na presente tese analisamos a influência da estrutura e heterogeneidade da vegetação sobre a diversidade em comunidades de aves do Cerrado. Nossa expectativa era corroborar a “Hipótese de Heterogeneidade de Habitats”, que propõe que quanto maior a estrutura e heterogeneidade da vegetação, maior será a diversidade de espécies. No primeiro capítulo, realizamos uma compilação sistemática de estudos publicados sobre a diversidade de aves em áreas ocupadas por algumas fisionomias típicas de Cerrado lato sensu, com o intuito de analisar o conhecimento obtido até então acerca da relação entre diversidade de aves e a estrutura da vegetação no Cerrado. Foram selecionadas 72 amostras de 22 estudos, sendo que estas amostras variaram quanto ao tipo fisionomia amostrada e o método amostral empregado, além de também estarem disponíveis em diferentes artigos e serem realizadas em diferentes regiões geográficas. Para análises destes dados, utilizamos a análise de modelos lineares generalizados de efeitos mistos (modelo com distribuição de erros poisson), que permite analisar os efeitos de variáveis fixas e aleatórias sobre a variável explicativa (riqueza de espécies). As variáveis fixas foram o tipo de vegetação amostrada (vegetação campestre, savânica e florestal) e o método amostral empregado (ponto fixo, transecto e redes de neblina). Já as variáveis de efeito aleatório utilizadas foram o estudo onde os dados foram publicados, o autor de cada estudo e a localidade geográfica. O efeito destas variáveis aleatórias poderiam afetar somente os interceptos das relações entre as variáveis fixas e a variável explicativa ou poderiam alterar a relação entre as variáveis fixas e explicativa. Construímos diversos modelos a partir da combinação de variáveis de efeito fixo e aleatório e a seleção do modelo mais parcimonioso foi feito por meio do critério AICc (critério de informação de Akaike corrigido para pequenas amostras). O modelo que apresentou menor valor de AICc (mais parcimonioso) foi aquele que incluiu os efeitos de ambas variáveis de efeito fixo (fisionomia e método amostral) e também um efeito da interação entre estas duas variáveis. Neste modelo também foram incluídos os efeitos das variáveis aleatórias estudo e localidade geográfica sobre os interceptos das relações entre as variáveis de efeito fixo e a variável explicativa. Estes resultados mostraram que a riqueza de espécies de aves em nosso estudo variou não só em função da fisionomia e do método amostral empregado, mas dependendo do método amostral utilizado a relação entre riqueza e fisionomia também foi alterada. Portanto, esta interação não permitiu que fosse estimada a relação entre fisionomia e riqueza sem considerar o efeito dos métodos. Já os efeitos das variáveis aleatórias mostraram que a variação estimada nos interceptos entre estudos foi duas vezes maior do que a variação estimada entre localidades geográficas. O efeito da interação entre as variáveis fisionomia e método amostral apontou para a existência de heterogeneidade de detecção entre locais com diferentes fisionomias, além também de um efeito das fisionomias na efetividade dos diferentes métodos amostrais. A influência dos métodos amostrais no número de espécies observadas em cada fisonomia pode ser esperada devido às diferenças intrínsecas dos métodos, já que ponto fixo e transecto são baseados em contatos visuais e auditivos com as espécies, enquanto que o método de rede de neblina consiste na captura passiva das espécies que voam na altura das redes. Assim, redes de neblina podem ser mais efetivas em habitats menos estruturados (por ex. campos limpos e sujos), onde a rede alcança quase todo os estratos de vegetação. No entanto, o método de transecto pode ser mais efetivo que o método de ponto fixo em áreas de florestas, pois nestes hábitats as espécies tendem a ter territórios menores e o deslocamento do observador proporciona ao observador cobrir um maior número de terrítórios. Por outro lado, o ponto fixo pode ser mais vantajoso por não produzir ruído e afugentar as espécies, o que pode ser uma desvantagem do método de transecto. Outros fatores, como a experiência e número de observadores, número de pontos amostrais, número de redes utilizadas e comprimento de transectos, podem explicar a grande variação estimada entre os estudos. Uma das maneiras de se contornar estes efeitos metodológicos é utilizar métodos desenvolvidos especialmente para lidar com diferentes probabilidades de detecção entre espécies, entre sítios e até métodos amostrais, o que poderia render dados mais confiáveis para o estudo da ecologia das espécies e para a elaboração de planos de manejo e/ou conservação. No segundo capítulo, a relação entre diversidade de aves e estrutura da vegetação foi analisada a partir de dados coletados em campo e utilizando um protocolo de amostragem específico para se estimar e considerar os efeitos da vegetação sobre a detecção das espécies. As amostragens foram realizadas em um dos maiores e mais preservados remanescentes de Cerrado (Parque Nacional Grande Sertão Veredas-PARNA GSV) e consistiram do registro das espécies de aves em 32 áreas dispostas em um gradiente de vegetação de Cerrado, que variaram desde campos limpos e sujos, campos cerrado a cerrados sensu stricto. O cálculo da riqueza de espécies de aves em cada sítio foi realizado através de modelos de ocupação-detecção, adaptados para estimar a riqueza de espécies em comunidades. A vegetação, por sua vez, foi medida a partir de estimativas de presença da vegetação entre 0 e 4 m de altura (16 intervalos de 22,5 cm cada um) e duas variáveis de estrutura foram obtidas a partir de uma análise de componentes principais, que foi aplicada para resumir a variação da presença de vegetação nos 16 intervalos de altura. Estas variáveis de vegetação foram relacionadas tanto com a ocupação quanto com a detecção das espécies, já que a estrutura da vegetação poderia influenciar não só a ocorrência mas também a detecção das espécies. O dia da amostragem e também a temperatura no momento da amostragem também foram incluídas como covariáveis que poderiam afetar a detecção. Após a estimativa da riqueza de espécies pelo modelo de ocupação-detecção para comunidades, esta riqueza estimada foi relacionada por uma função quadrática com a estrutura da vegetação usando um modelo bayesiano de metanálise, que permitiu incluir a incerteza nas estimativas de riqueza na análise. A título de comparação, também foi ajustado um modelo quadrático GLM (distribuição de erros normal) aos dados de riqueza observada. Os resultados mostraram que a riqueza estimada a partir dos dados das 38 espécies mais detectadas durante as amostragens teve uma fraca relação com as duas covariáveis de estrutura de vegetação, sendo que houve uma maior riqueza de espécies em sítios com vegetação intermediária em altura e uma maior riqueza de espécies de aves em sítios onde houve maior presença de vegetação abaixo de 2 m de altura. No entanto, as relações entre riqueza estimada e estas covariáveis foi menos intensa mas qualitativamente similar às relações entre a riqueza observada e as covariáveis de vegetação. A menor intensidade nas relações da riqueza estimada foi evidenciada principalmente em ambos os extremos do gradiente de estrutura vertical da vegetação e também nas áreas com menor presença de vegetação abaixo de 2 m. Estes resultados mostraram que o efeito da detecção pode alterar o efeito da relação entre riqueza de espécies e estrutura de vegetação. Além disso, ao menos para as 38 espécies mais comumente encontradas na área de estudo, os resultados apontam para a importância de todo o gradiente de estrutura da vegetação para a manutenção da riqueza de espécies de aves no Cerrado. Futuros estudos que visem aprimorar o uso destes modelos de ocupação e detecção para comunidades são fundamentais para permitir o uso dos dados de todas as espécies da comunidade. Além disto, outros estudos que se proponham a analisar a dinâmica e composição das comunidades de aves nestes gradientes de estrutura de vegetação são fundamentais para um maior conhecimento sobre a ecologia e conservação das aves no Cerrado / In several studies around the globe, the structure and diversity of vegetation have been shown to be a determining factor in the diversity of species of birds and also other groups of animals. The Cerrado is the second most extensive and most threatened biome occurrence in Brazil. This biome is also characterized by an obvious environmental gradient of vegetation structure and heterogeneity. In this thesis we analysed the influence of the structure and diversity of the vegetation on the diversity in the Cerrado bird communities. Our expectation was to support the “Habitat Heterogeneity Hypothesis” which suggests that the higher the structure and diversity of vegetation, the greater the diversity of species. In the first chapter, we conducted a systematic compilation of published studies on the diversity of birds in areas occupied by some typical physiognomy of Cerrado textit lato sensu, in order to analyze the knowledge obtained so far about the relationship between diversity of birds and the structure of the vegetation in the Cerrado. We selected 72 samples from 22 studies, and these samples varied as the sampled vegetation physiognomy, the sampling method used, and they also are available in different articles and be carried out in different geographical regions. We performed the analysis of generalized linear mixed effects models (model poisson distribution errors), which allows us to analyse the effects of fixed and random variables on the explanatory variable (species richness). Fixed variables were the type of sampled vegetation (grassland, savanna and forest) and the sample method employed (fixed point, transect and mist nets). The random variables used were the study where the data were published, the author of each study and geographic location. These random variables could only affect the intercepts of the relationship between fixed and variable explanatory variable or could alter the relationship between fixed and explanatory variables. We built several models from the combination of fixed and random effects variables and selection the most parsimonious model was made by the AIC criterion (Akaike information criterion corrected for small samples). The model that showed lower value of AIC (more parsimonious) was the one that included the effects of both fixed effect variables (physiognomy and sampling method) and also an effect of the interaction between these two variables. In this model were also included the effects of random variables study and geographic location of the intercepts of the relationship between the fixed effect variables and the explanatory variable. These results showed that the bird species richness in our study varied not only in terms of physiognomy and sample method, but depending on the sampling method used the relationship between richness and physiognomy has also changed. Therefore, this interaction does not allowed us to estimate the relationship between physiognomy and richness without considering the effect of the methods. Since the effects of random variables showed that the variation in the estimated intercept between studies was twice larger than the estimated variation between geographic locations. The effect of interaction between the vegetation physiognomy and sampling method variables pointed to the existence of heterogeneity detection between locations with different physiognomies, in addition also of an effect of the physiognomies in the effectiveness of different sampling methods. The influence of the sampling method in the number of species observed in each physiognomy may be expected due to intrinsic differences in the methods, since fixed point counts and transect are based on visual and aural contacts with the species, while the mist net method consists in passive capture of species flying at the time of the networks. Thus, mist nets may be more effective in less structured environments (eg. Clean and dirty fields) where the net reaches virtually all vegetation layers. However, transect method can be more effective than the fixed point method in areas of forests since in these habitats species tend to have smaller territory areas, and the observer movement provides the observer cover greater areas. On the other hand, the point counts can be more advantageous not to produce noise and chase species, which may be a disadvantage of transect method. Other factors, such as experience and number of observers, the number of sampling points, the number of nets used and length of transects, may explain the wide variation between studies estimated. One of the ways to overcome these methodological effects is to use methods developed especially to deal with different probabilities of detection of species, between sites and sampling methods, which could yield more reliable data for the ecological study of the species and the development of management plans and/or conservation. In the second chapter, the relationship between diversity of birds and vegetation structure was analysed from data collected in the field and using a specific sampling protocol to estimate and consider the effects of vegetation on the detection of species. The samples were taken in one of the largest and well preserved remnants of Cerrado (Grande Sertão Veredas National Park-PARNA GSV) and consisted of the record of bird speciesin 32 areas arranged in a Cerrado vegetation gradient, ranging from grasslands, open and dense savannas. The calculation of the bird species richness at each site was conducted using occupancy-detection models adapted to estimate the number of species in communities. The vegetation, in turn, was measured from estimates of the presence of vegetation in height intervals between 0 and 4 m (16 intervals of 22.5 cm each) and two structure variables were obtained from a principal component analysis applied to summarize the variation of the vegetation presence in height intervals. These vegetation variables were related to both the occupation and detection of species, since the vegetation structure could influence not only the occurrence but also the detection of species. The day of sampling and also the temperature at the time of sampling were also included as covariates that may a_ect the detection. After the estimation of species richness by model occupancy detection for communities, this estimated richness was related by a quadratic function with the vegetation structure using a Bayesian meta-analysis model, which allowed us include uncertainty in richness estimates. By way of comparison, we also fit a quadratic model GLM (normal distribution errors) to the observed richness data. The results showed that the richness estimated from the data of the 38 most detected species during sampling had a weak relationship with both covariates vegetation structure, and there was a greater number of species at sites with intermediate vegetation height and greater bird species richness in places where there was a greater presence of vegetation below 2 m in height. However, relations between estimated richness and these covariates was less intense but qualitatively similar to the relationship between observed richness and vegetation covariates. The lowest intensity in the estimated richness relationship was observed mainly at both ends of the vertical gradient of vegetation and also in areas with less presence of vegetation below 2 m. These results showed that the effect of detection can change the effect of the relationship between species richness and vegetation structure. Moreover, at least for the 38 species most commonly found in the study area, the results point to the importance of the entire vegetation structure gradient to maintain the bird species richness in Cerrado. Future studies aiming to improve the use of these models of occupation and detection for communities are essential to allow the use of data of all species in the community. In addition, other studies that propose to analyse the dynamics and composition of bird communities in these vegetation structure gradients are fundamental for a better understanding of the ecology and conservation of Cerrado birds

Made available in DSpace on 2014-07-29T15:23:42Z (GMT). No. of bitstreams: 1 Dissertacao Amanda Goulart de Oliveira Sousa.pdf: 1097784 bytes, checksum: efe44a45c995339f0d2e83886704fc64 (MD5) Previous issue date: 2011-04-01 / The aim of this study was to determine the nutritional quality and protein value of the baru almond, pequi almond, and cerrado cashew nut, native fruits from the Brazilian Savanna, compared to the peanut. Standardized methods were used to determine centesimal composition, amino acid profile, fatty acids and mineral content. The experiment was carried out with 42 male weanling Wistar rats. The animals were randomly assigned into seven groups. The experiment lasted fourteen days. The diets were formulated according to AIN-93G, six diets with 10% protein: CAS7 (7% lipid casein), CAS15 (15% lipid casein), AMB (baru almond), AMP (pequi almond), CJC (cerrado cashew nut), AMD (peanut) and a protein-free diet. A biological assay was carried out to assess the protein value, by Net Protein Ratio (NPR), Relative Net Protein Ratio (RNPR), and Protein Digestibility-Corrected Amino Acid Score (PDCAAS) methods. We found that the exotic almonds and the nut are rich in proteins (22.7 29.9 g/100 g), lipids (41.9 50.0 g/100 g), fibres (baru and pequi almonds, around 10.0 g/100 g), iron and zinc (4.3 7.4 mg/100 g). Baru almond s protein did not show deficiency in essential amino acids and lysine was the first limiting amino acid in the proteins of the pequi almond and cerrado cashew nut. The baru almond showed a RNPR of 86%, similar to that of the cerrado cashew nut (78%), but higher than that of the peanut (72%) and of the pequi almond (54%). The PDCAAS value of the baru almond (91%) was the highest and cerrado cashew nut and peanut presented similar values of this index (82%), which were higher than that of the pequi almond (55%). The baru almond has the highest protein quality, but the cerrado cashew nut and peanut are sources of good quality protein, too. We recommend the inclusion of these exotic foods in healthy diets and in food industry, and the baru almond and cerrado cashew nut as sources of complementary protein. / O objetivo deste estudo foi determinar a qualidade nutricional e o valor protéico das amêndoas de baru e de pequi e da castanha-de-caju-do-cerrado, frutas nativas do Cerrado brasileiro, e comparar com o amendoim. Determinou-se a composição química centesimal, teor de minerais e perfil de aminoácidos, conforme métodos padronizados. Foi realizado um experimento com 42 ratos Wistar, machos, recém-desmamados, distribuídos em sete grupos segundo delineamento por blocos casualizados, durante catorze dias. As dietas foram formuladas segundo AIN-93G, sendo seis dietas com 10% de proteína: CAS7 (caseína com 7% de lipídios); CAS15 (caseína com 15% de lipídios); amêndoas de baru (AMB); amêndoa de pequi (AMP); castanha-de-caju-do-cerrado (CJC) e amendoim (AMD), e uma dieta aprotéica (APO). O valor protéico foi estimado por meio dos métodos Net Protein Ratio (NPR), Relative Net Protein Ratio (RNPR) e Protein Digestibility-Corrected Amino Acid Score (PDCAAS). As amêndoas de baru, de pequi e a castanha-de-caju-do-cerrado são ricas em proteínas (22,7-29,9 g/100 g), lipídios (41,9-50,0 g/100 g), fibras (amêndoas de baru e de pequi, em torno de 10,0 g/100 g), ferro e zinco (4,3-7,4 mg/100 g). A proteína da amêndoa de baru não apresentou deficiência em aminoácidos essenciais, e a lisina foi o primeiro aminoácido limitante nas proteínas da amêndoa de pequi e da castanha-de-caju-do-cerrado, e o segundo limitante na proteína do amendoim. A amêndoa de baru apresentou RNPR de 86%, estatisticamente similar ao da castanha-de-caju-do-cerrado (78%), mas superior ao do amendoim (72%) e da amêndoa do pequi (54%). A amêndoa de baru apresentou maior valor de PDCAAS (91%), e a castanha-de-caju-do-cerrado e o amendoim apresentaram valores semelhantes para este índice (82%), seguidos pela amêndoa de pequi (55%). A amêndoa de baru possui maior qualidade protéica, porém a castanha-de-caju-do-cerrado e o amendoim também são fontes de proteína de boa qualidade. Recomendamos a inclusão destes alimentos nativos em dietas saudáveis e na indústria alimentícia, e a amêndoa de baru e a castanha-de-caju-do-cerado como fontes de proteínas complementares.