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An investigation into the effects of deforestation and habitat fragmentation on a central Amazonian frog community was carried out on the Biological Dynamics of Forest Fragments Project, (BDFFP) based in Manaus, Amazonas, Brazil. Three aspects of deforestation were investigated: the effects of fragmentation and reserve size, the influence of matrix habitat and the effects offorest edge on frogs in 10- hectare isolates. Very few frogs species were lost from fragments (regardless of size) following fragmentation and isolation for 7-10 years. Instead, frog species richness increased, with an average increase in 10 species per fragment. The increase in species was brought about by an increase in matrix associated species, some of which were present in the absence of their preferred breeding habitat. Different frog species had varied responses to fragmentation. The abundance of Eleutherodactylus fenestratus, a terrestrial breeder, increased significantly as fragment size decreased, and its abundance was significantly higher in both large and small fragments than in continuous forest. Colostethus stepheni, a semi-terrestrial breeder, was less abundant in fragments than continuous forest. Finally, Eleutherodactylus zimmermanae and Osteocephalus sp.A did not differ significantly in abundance among fragments, or between fragments and continuous forest. Multiple regression analysis indicated that variation in litter depth and canopy cover may explain the observed increase in E. fenestratus abundance in small fragments. Breeding success of pool breeders attracted to artificial pools was variable, but there was no evidence of reduced breeding success in fragments relative to primary forest. Overall, fragmentation appeared to affect the frog community less severely than other taxonomic groups. Species richness in tropical forest remnants showed a tendency to increase as a result of fragmentation, and only one of four species exhibited lowered abundance in fragments. The effects of fragmentation and subsequent small isolated populations of frog species in fragments was alleviated somewhat by the ability of central Amazonian frogs to utilise matrix habitat. Litter frogs, wallow breeders and upland forest pool breeders all displayed an ability to permeate, and in most cases become residents of matrix habitat. Both matrix with a history of cut and burn and matrix which was only cut supported a similar frog community. Thus, for central Amazonian frogs isolates were not truly isolated due to the ability of frogs to utilise matrix habitat. Litter frogs in 10- hectare isolates displayed an independence from edge related abiotic and biotic gradients. This independence was true for frog species richness, abundance and composition. Consequently, forest fragments are in effect larger for frogs than for other taxa who are constrained by edge effects to exist only within the core of large fragments. Colostethus stepheni was one species found to be negatively affected by habitat fragmentation. Abundance of Colostethus stepheni was significantly lower in fragments and matrix habitat compared to primary continuous forest. This species was also found to be sensitive to edge, with higher abundances recorded as distance from the edge increased. The community level approach adopted in this study, as opposed to intensive investigation of single species, may well have overlooked other' sensitive' species which show more subtle responses to habitat fragmentation than that of Colostethus stepheni. The ability to use matrix and the relative independence from edge related phenomena accounts for the resilience of central Amazonian frogs in a disturbed and fragmented landscape. However, with respect to matrix habitat, forest surveyed in this study has not been repeatedly cut or cut and burnt (with the exception of pasture-land where the frog community is depauperate). In other areas of the Amazon, away from the experimental plots of the BDFFP, matrix habitat is destroyed more frequently. More work is needed to determine the ability of central Amazonian frogs to utilise matrix habitat which is disturbed more frequently.

An investigation into the effects of deforestation and habitat fragmentation on a central Amazonian frog community was carried out on the Biological Dynamics of Forest Fragments Project, (BDFFP) based in Manaus, Amazonas, Brazil. Three aspects of deforestation were investigated: the effects of fragmentation and reserve size, the influence of matrix habitat and the effects offorest edge on frogs in 10- hectare isolates. Very few frogs species were lost from fragments (regardless of size) following fragmentation and isolation for 7-10 years. Instead, frog species richness increased, with an average increase in 10 species per fragment. The increase in species was brought about by an increase in matrix associated species, some of which were present in the absence of their preferred breeding habitat. Different frog species had varied responses to fragmentation. The abundance of Eleutherodactylus fenestratus, a terrestrial breeder, increased significantly as fragment size decreased, and its abundance was significantly higher in both large and small fragments than in continuous forest. Colostethus stepheni, a semi-terrestrial breeder, was less abundant in fragments than continuous forest. Finally, Eleutherodactylus zimmermanae and Osteocephalus sp.A did not differ significantly in abundance among fragments, or between fragments and continuous forest. Multiple regression analysis indicated that variation in litter depth and canopy cover may explain the observed increase in E. fenestratus abundance in small fragments. Breeding success of pool breeders attracted to artificial pools was variable, but there was no evidence of reduced breeding success in fragments relative to primary forest. Overall, fragmentation appeared to affect the frog community less severely than other taxonomic groups. Species richness in tropical forest remnants showed a tendency to increase as a result of fragmentation, and only one of four species exhibited lowered abundance in fragments. The effects of fragmentation and subsequent small isolated populations of frog species in fragments was alleviated somewhat by the ability of central Amazonian frogs to utilise matrix habitat. Litter frogs, wallow breeders and upland forest pool breeders all displayed an ability to permeate, and in most cases become residents of matrix habitat. Both matrix with a history of cut and burn and matrix which was only cut supported a similar frog community. Thus, for central Amazonian frogs isolates were not truly isolated due to the ability of frogs to utilise matrix habitat. Litter frogs in 10- hectare isolates displayed an independence from edge related abiotic and biotic gradients. This independence was true for frog species richness, abundance and composition. Consequently, forest fragments are in effect larger for frogs than for other taxa who are constrained by edge effects to exist only within the core of large fragments. Colostethus stepheni was one species found to be negatively affected by habitat fragmentation. Abundance of Colostethus stepheni was significantly lower in fragments and matrix habitat compared to primary continuous forest. This species was also found to be sensitive to edge, with higher abundances recorded as distance from the edge increased. The community level approach adopted in this study, as opposed to intensive investigation of single species, may well have overlooked other' sensitive' species which show more subtle responses to habitat fragmentation than that of Colostethus stepheni. The ability to use matrix and the relative independence from edge related phenomena accounts for the resilience of central Amazonian frogs in a disturbed and fragmented landscape. However, with respect to matrix habitat, forest surveyed in this study has not been repeatedly cut or cut and burnt (with the exception of pasture-land where the frog community is depauperate). In other areas of the Amazon, away from the experimental plots of the BDFFP, matrix habitat is destroyed more frequently. More work is needed to determine the ability of central Amazonian frogs to utilise matrix habitat which is disturbed more frequently.

Made available in DSpace on 2015-04-13T12:17:12Z (GMT). No. of bitstreams: 1 maria.pdf: 1630908 bytes, checksum: a42167665f1996abf949ba4821f67f8c (MD5) Previous issue date: 2012-10-25 / Atualmente, é notória a importância das florestas tropicais para o equilíbrio ambiental do planeta. No entanto, também, pode ser observada uma degradação contínua dessas áreas como conseqüência da exploração madeireira desordenada e da ampliação das áreas de pecuária. Na tentativa de reduzir esse problema, os gestores públicos têm usado de vários métodos, um desses métodos são os subsídios verdes , que constam, basicamente, da concessão de remunerações em espécie para os habitantes dessas áreas com o objetivo de compensá-los pelo não uso direto da floresta, como exemplo pode ser citado o programa ambiental denominado Bolsa Floresta adotado no estado do Amazonas. Por outro lado, tem-se observado em alguns casos, que mesmo após a aceitação da compensação monetária, os habitantes dessas áreas continuam desmatando a floresta alegando que o valor pago não corresponde à receita obtida no passado com o uso direto da floresta. Por conta disso, a presente pesquisa tem como objetivo principal verificar se existe diferença significativa entre o valor percebido pelos habitantes da Reserva de Desenvolvimento Sustentável do Uatumã e o valor pago pelo programa Bolsa Floresta . A metodologia utilizada na pesquisa será o Método de Valoração Contingente (MVC) que se baseia na percepção das pessoas para valorar os ativos e passivos ambientais, para isso será utilizada uma amostra correspondente a 82 entrevistados, derivada de um tamanho populacional de 380 famílias existentes na RDS do Uatumã, considerando um nível de confiança de 95% e uma margem de erro máxima permitida de 8%. De acordo com os resultados obtidos pode-se concluir que existe diferença significativa entre o valor percebido pelos habitantes da Reserva de Desenvolvimento Sustentável do Uatumã e o valor pago pelo programa Bolsa Floresta, sendo o valor estimado de R$ 200,00/família/mês. Isso indica que ajustes deveriam ser feitos no programa para alcançar melhore resultados.

Malgré l'importance reconnue des forêts tropicales humides dans la régulation du climat et du cycle global du carbone, la biogéochimie des forêts tropicales reste moins bien appréhendée que celle d'autres biomes. En particulier, il existe encore de larges incertitudes quant aux limitations nutritives des processus ou encore sur le rôle de la diversité pour les fonctions écosystémiques. La diversité spécifique élevée des arbres de forêt amazonienne se traduit localement par une forte hétérogénéité de la qualité des apports de litière foliaire, ces apports constituant une ressource primordiale d'énergie et de nutriments pour les organismes saprophages. Cependant les conséquences d'une telle hétérogénéité des litières pour le fonctionnement souterrain sont encore peu connues dans ce milieu. L'objectif de cette thèse est d'établir une compréhension mécaniste des effets de la qualité des apports de litière ainsi que du rôle de leur diversité sur la décomposition. J'ai combiné des fertilisations factorielles de carbone (C), d'azote (N) et de phosphore (P) à l'utilisation d'une large gamme de stœchiométrie C : N : P des litières (issues de différentes espèces d'arbres) en forêt tropicale de Guyane française et en laboratoire pour évaluer la nature et l'étendue des contraintes énergétiques et nutritives imposées par la qualité des litières sur les activités des décomposeurs. Bien que la perte en masse des litières dans ce système d'étude apparait largement expliquée par la qualité des différentes formes de C des litières, suggérant un fort contrôle de la disponibilité en énergie sur la décomposition, les ajouts externes de C n'ont pas permis de mettre en évidence cette apparente contrainte énergétique. Cependant, je montre que la décomposition des litières tropicales est limitée conjointement par N et P, et que l'amplitude de cette co-limitation est fortement reliée à la disponibilité en P des litières ainsi qu'à leur stœchiométrie N : P. Ainsi, même si le P apparaît plus profondément limitant dans ce système (en accord avec l'hypothèse généralement admise d'un fort déficit en P en forêt tropicale humide), l'accès à l'N foliaire semble également contraindre la décomposition. Je mets également en évidence des effets de diversité des mélanges de litières, pour la plupart synergiques (les taux de décomposition observés des mélanges étaient généralement plus élevés que ceux prédits à partir des taux de décomposition des espèces seules) et largement amplifiés par la présence de la faune détritivore. De plus, en présence de faune, il apparait qu'une forte dissimilarité stœchiométrique dans les mélanges de litières favorise des effets synergiques. Autrement dit, l'association de litières ayant des stœchiométries dissimilaires semble favoriser un meilleur équilibre nutritionnel pour la faune saprophage, stimulant ainsi la décomposition. Finalement, je montre que ces effets synergiques dans les mélanges sont renforcés à travers les effets à long terme des apports de litières issus des différentes espèces d'arbres contribuant à ces mélanges. Ce résultat suggère que la complémentarité de l'utilisation des ressources émerge à travers des interactions à long terme entre les arbres et les organismes décomposeurs. / The high tree species diversity in Amazonian rainforest translates into a high variation of leaf litter quality input to the soil. These inputs constitute a major resource of nutrients and energy for saprophageous organisms, particularly in tropical rainforests growing on old and highly weathered soils and consequently impoverished in rock-derived mineral nutrients. However the consequences of such leaf litter heterogeneity for belowground functioning are still poorly understood. In this thesis, I aim to develop a better mechanistic understanding of leaf litter quality effects and litter diversity on decomposition. Using a factorial fertilization of carbon (C), nitrogen (N), phosphorus (P) and a wide range of leaf litter C : N : P stoichiometries (derived from different tree species) in French Guiana rainforest and in laboratory, I aim to assess the nature and the extent of energetic and nutritional constraints imposed by litter quality on decomposer activities. Although the litter mass loss in this study system is greatly explained by the litter C quality, suggesting a strong control of energy availability on decomposition, external C additions do not alleviate this apparent energetic constraint. However, I find that litter decomposition is conjointly limited by N and P and that the extent of this NP co-limitation is widely related to leaf litter P content and to litter N : P stoichiometry. Thus, even if P appears more profoundly limiting in this system (in accordance to the well-recognized P deficiency hypothesis in tropical rainforest), the litter N access seems also constrain the decomposition. Moreover, I find significant litter diversity effects in litter mixtures and most of them are synergistics (observed mass loss in mixture was more often higher than predicted mass loss on the basis of single species decomposition). These litter diversity effects are largely higher in presence of soil fauna and increase with stoichiometric dissimilarity in mixtures. In other words, the association of stoichiometrically dissimilar litter appear promote a better nutritional balance for the saprophageaous fauna, and thus, stimulate the decomposition. Finally, I show that synergistic effects in mixtures are reinforced toward long-term presence of tree species contributing to the litter mixtures. This result suggest that complementarity effects on mixed litter decomposition may emerge through long-term interactions between aboveground and belowground biota.