4 resultados para FOREST FRAGMENTS

em Universidad Politécnica de Madrid


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Muchos estudios han descrito la composición y diversidad de los bosques montanos tropicales, pero los patrones espaciales y las diferentes tipos de relaciones de estos, entre especies o entre grupos funcionales ha sido poco documentada. El presente trabajo se realizó en tres parcelas completamente censadas del bosque de la Estación Biológica “Chamusquin” (Zamora Chinchipe, Ecuador), y se plantea como objetivo principal conocer la estructura espacial y dinámica del bosque montano tropical del sur del Ecuador, así como las interacciones bióticas y limitaciones abióticas que influyen en esta dinámica, para ello se planteó cuatro objetivos de estudio que son: conocer los patrones espaciales de los gremios ecológicos dentro de la zona de estudio; conocer la influencia de la dependencia negativa de la densidad sobre dos especies de helechos arborescentes (Cyatheaceae); conocer si existen especies o grupos ecológicos acumuladoras o repulsoras de diversidad en el área de estudio; y conocer cómo influyen la diversidad filogenética y la densidad del vecindario en la incidencia de herbivoría y parasitismo sobre las fases iniciales del establecimiento forestal (brinzales) así como en la supervivencia de los mismos Como paso previo para el análisis del resto de objetivos, dentro de cada parcela se marcaron todos los individuos con DAP ≥5 cm y se tomaron sus coordenadas (X, Y). Además se tomaron datos de variables superficiales y muestras del suelo. Las especies encontradas se clasificaron de acuerdo a sus características biológicas, asignándolas a cada uno de los cuatro gremios forestales usualmente distinguidos en los bosques tropicales: tolerantes a la sombra (TS), tolerantes parciales a la sombra (TPS), pioneras de vida larga (PVL) y pioneras de vida corta (PVC). Para el estudio del primer objetivo tas se emplearon funciones K de Ripley inhomogéneas, ajustando la heterogeneidad en base a la variación espacial de las variables ambientales registradas . Los resultados demostraron que tanto la frecuencia relativa como el patrón espacial de las diferentes estrategias funcionales varían a lo largo de la sucesión y que éste además está influido por la variación ambiental. En adición, tanto el patrón espacial como la respuesta a la variación ambiental de los diferentes gremios es distinta entre adultos y juveniles. Todo ello sugiere que el ensamblaje de la diversidad en los bosque montanos andinos está controlado por procesos deterministas más que por procesos neutrales. Para responder el segundo objetivo se estudiaron los efectos de la dependencia negativa de la densidad (DND) y la heterogeneidad ambiental en las poblaciones de dos especies de helechos arborescentes abundantes, Cyathea caracasana y Alsophila engelii, y cómo estos efectos cambian a través de un gradiente sucesional. Los patrones de especies albergan información sobre procesos tales como la competencia que puede ser revelado fácilmente utilizando técnicas de análisis de patrones punto. Sin embargo, su detección puede ser difícil debido a los efectos de factores de confusión heterogeneidad del hábitat. Aquí, empleamos funciones K y funciones de correlación de par homogéneas y no homogéneas para cuantificar el cambio en el patrón espacial de diferentes clases de tamaño con un diseño de casos-controles para estudiar las asociaciones entre helechos arborescentes jóvenes y adultos. Usando estimaciones espaciales de la biomasa de los cuatro tipos de gremios ecológicos (PVC, PVL, TPS, TS) como covariables, hemos ajustado modelos de Poisson heterogéneos a los patrones de puntos de de los helechos juveniles y los adultos y hemos explorado además la existencia de dependencia del hábitat en estos patrones. Nuestro estudio reveló efectos de la DND para C. caracasana y un fuerte filtrado ambiental que subyace al patrón de A. engelii. Encontramos también que las poblaciones de adultos y juveniles de ambas especies respondieron de manera diferente a la heterogeneidad del hábitat y en la mayoría de los casos esta heterogeneidad se asoció con la distribución espacial de la biomasa de los cuatro tipos de gremios. Estos resultados muestran la eficacia de controlar los efectos de la heterogeneidad ambiental para evitar su confusión con los patrones derivados de interacciones biológicas cuando se estudia la DND y demuestran la utilidad de los mapas de covariables derivados de comunidades biológicas como resumen de la heterogeneidad ambiental. Para nuestro tercer objetivo nos centramos en explorar cómo influyen las especies más abundantes en la organización espacial de la diversidad a lo largo de un gradiente sucesional en el bosque montano del sur del Ecuador. Para ello utilizamos la función ISAR (Individual Species Area Relationship). Encontramos que la frecuencia de especies neutras, repulsoras y acumuladoras de diversidad taxonómica varía dependiendo del grado de sucesión. Además se comprobó que la mayoría de los gremios forestales se comportó de forma neutral, pero la proporción de acumuladores, aumentó al avanzar la sucesión hacia estados más maduros, lo que indica el establecimiento de fuertes procesos competitivos a medida que avanza la sucesión y la mayor importancia del papel de las especies individuales en dichos estados. Finalmente, examinamos el efecto de la vecindad taxonómica y filogenética, así como la estrategia de vida, sobre la incidencia de la herbivoría y el parasitismo en las poblaciones de brinzales de tres fragmentos forestales en una secuencia sucesional del bosque montano húmedo. Evaluamos además los efectos de herbivoría, parasitismo, estrategia de vida y diferentes indicadores de la vecindad sobre la supervivencia de los brinzales. Por último contrastamos la posible existencia de una tendencia compensatoria de la comunidad (CCT) a nivel de fragmento forestal. Nuestros análisis no consiguieron detectar una CCT pero si pusieron de manifiesto la existencia de efectos locales de dependencia negativa de la densidad. Por ejemplo, la presencia de herbivoría y parasitismo sobre los brinzales se relacionó significativamente con una menor supervivencia de estos. Por otro lado, indicadores del efecto de la vecindad como la densidad de brinzales del mismo género y el área basal de árboles vecinos del mismo género incrementaron la prevalencia de la herbivoría o el parasitismo en los brinzales. El incremento de la incidencia de la herbivoría o el parasitismo no está exclusivamente ligado a tener una vecindad taxonómicamente idéntica (vecinos de la misma especie) sino que categorías taxonómicas más laxas como el "género" o simplemente relaciones de semejanza filogenética son capaces de predecir los efectos negativos de la vecindad. Los efectos detectados variaron en los diferentes grupos funcionales distinguidos. Los resultados que hemos obtenido en este trabajo parecen indicar que el funcionamiento de las comunidades de brinzales del bosque montano tropical no difiere mucho del reportado para comunidades de plántulas en otros bosques tropicales y cumple las predicciones de la hipótesis de Janzen y Connell, aunque matizadas por la mayor resistencia de los brinzales al efecto de herbivoría y parasitismo. ABSTRACT Many studies have described the composition and diversity of tropical montane forests, but the different spatial patterns and types of relationships between species or between functional groups has been poorly documented. This work was made in three completely surveyed forest plots at Biological Station "Chamusquin" (Zamora Chinchipe, Ecuador). Our main objective was to know the spatial structure and dynamics of the tropical montane forest in southern Ecuador, as well as the biotic interactions and abiotic constraints affecting this dynamic. More specifically, we aimed to understand the spatial patterns of ecological guilds; to explore the influence of negative density dependence on two species of tree ferns (Cyatheaceae); to determine whether some species or ecological groups structure spatially plant diversity in these forests; and to test the effects of biological neighborhood on the incidence of herbivory and parasitism and on the survival of saplings. We mapped within each plot all trees with DBH ≥5 cm. Besides, surface data variables and soil samples they were taken. The species found were classified according to their biological characteristics in four forest guilds: shade-tolerant (ST), partial shade tolerant (PST), long-lived pioneer (LLP) and short-lived pioneer (SLP). To analyze the spatial patterns of the ecological guilds, we employed the inhomogeneous version of Ripley's K-function and adjusted heterogeneity surfaces based on the spatial variation of the measured environmental variables. The results showed that both the relative frequency of each functional guild as well as their spatial pattern varied throughout succession and that the spatial pattern is explained by environmental variation. In addition, both spatial pattern and the response to spatial variation of each guild varied throughout ontogeny. All in all suggest that diversity assembly in the studied forests is ruled by deterministic instead of neutral processes. We also addressed the negative effects of density dependence (NDD) and environmental heterogeneity in populations of two species of abundant tree ferns, Cyathea caracasana and Alsophila engelii, and how these effects change across a successional gradient.. Here, we used homogeneous and inhomogeneous K and pair-correlation functions to quantify the change in the spatial pattern of different size classes with a case-control design to study associations between young and adult tree ferns. Using spatial estimates of the biomass of the four types of ecological guilds (SLP, LLP, PST, ST) as co-variables, we fitted heterogeneous Poisson models to juvenile and adult tree fern point patterns and explored the existence of habitat dependence. Our study revealed NDD effects for C. caracasana and strong environmental filtering underlying the pattern of A. engelii. We found that adult and juvenile populations of both species responded differently to habitat heterogeneity and in most cases this heterogeneity was associated with the spatial distribution of biomass of the four functional tree types. These findings show the effectiveness of factoring out environmental heterogeneity to avoid confounding factors when studying NDD and demonstrate the usefulness of covariate maps derived from mapped communities. For our third objective we focused on exploring how the most abundant species influence the spatial organization of tree diversity in these forests. For this, we used the individual species-area relationship function (ISAR). We found that the proportion of accumulator, repeller and neutral species, varied depending on the degree of succession. We found also that most guilds behaved neutrally but the proportion of accumulator guilds increased as succession advanced to more mature stages. This point, to the existence of strong competitive effects mediated by individual species in these mature forests. Finally, we examined the effects of life strategies and taxonomic and phylogenetic neighborhood on the incidence of herbivory and parasitism in the communities of saplings in the same forest fragments. We evaluated also the effects of life strategies, herbivory, parasitism and some indicators of neighborhood on sapling survival. Finally we tested for the existences of a compensatory community trend at plot scale. We did not found a CCT but we found proof of local NND effects. For instance, the prevalence of herbivory and parasitism were related to lower sapling survival. On the other hand the density of con-generic saplings and the basal area of neighbor con-generic trees were related to a higher prevalence of herbivory or parasitism in the saplings. We demonstrated that the increase in the prevalence of herbivory or parasitism it s not exclusive of a conspecific neighborhood but instead larger taxonomic categories such as "genus" or simple phylogenetic relationships are also able to predict NND effects. The NND effects varied among functional guilds. Our results show that the dynamic of sapling communities in Ecuadorian montane forests is similar to seedling dynamics in other tropical forest and follows the predictions of Janzen-Connell hypothesis, although softened by the strong resilience of saplings in comparison to seedlings.

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Persistence and abundance of species is determined by habitat availability and the ability to disperse and colonize habitats at contrasting spatial scales. Favourable habitat fragments are also heterogeneous in quality, providing differing opportunities for establishment and affecting the population dynamics of a species. Based on these principles, we suggest that the presence and abundance of epiphytes may reflect their dispersal ability, which is primarily determined by the spatial structure of host trees, but also by host quality. To our knowledge there has been no explicit test of the importance of host tree spatial pattern for epiphytes in Mediterranean forests. We hypothesized that performance and host occupancy in a favourable habitat depend on the spatial pattern of host trees, because this pattern affects the dispersal ability of each epiphyte and it also determines the availability of suitable sites for establishment. We tested this hypothesis using new point pattern analysis tools and generalized linear mixed models to investigate the spatial distribution and performance of the epiphytic lichen Lobaria pulmonaria, which inhabits two types of host trees (beeches and Iberian oaks). We tested the effects on L. pulmonaria distribution of tree size, spatial configuration, and host tree identity. We built a model including tree size, stand structure, and several neighbourhood predictors to understand the effect of host tree on L. pulmonaria. We also investigated the relative importance of spatial patterning on the presence and abundance of the species, independently of the host tree configuration. L. pulmonaria distribution was highly dependent on habitat quality for successful establishment, i.e., tree species identity, tree diameter, and several forest stand structure surrogates. For beech trees, tree diameter was the main factor influencing presence and cover of the lichen, although larger lichen-colonized trees were located close to focal trees, i.e., young trees. However, oak diameter was not an important factor, suggesting that bark roughness at all diameters favoured lichen establishment. Our results indicate that L. pulmonaria dispersal is not spatially restricted, but it is dependent on habitat quality. Furthermore, new spatial analysis tools suggested that L. pulmonaria cover exhibits a distinct pattern, although the spatial pattern of tree position and size was random.

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Persistence and abundance of species is determined by habitat availability and the ability to disperse and colonize habitats at contrasting spatial scales. Favourable habitat fragments are also heterogeneous in quality, providing differing opportunities for establishment and affecting the population dynamics of a species. Based on these principles, we suggest that the presence and abundance of epiphytes may reflect their dispersal ability, which is primarily determined by the spatial structure of host trees, but also by host quality. To our knowledge there has been no explicit test of the importance of host tree spatial pattern for epiphytes in Mediterranean forests. We hypothesized that performance and host occupancy in a favourable habitat depend on the spatial pattern of host trees, because this pattern affects the dispersal ability of each epiphyte and it also determines the availability of suitable sites for establishment. We tested this hypothesis using new point pattern analysis tools and generalized linear mixed models to investigate the spatial distribution and performance of the epiphytic lichen Lobaria pulmonaria, which inhabits two types of host trees (beeches and Iberian oaks). We tested the effects on L. pulmonaria distribution of tree size, spatial configuration, and host tree identity. We built a model including tree size, stand structure, and several neighbourhood predictors to understand the effect of host tree on L. pulmonaria. We also investigated the relative importance of spatial patterning on the presence and abundance of the species, independently of the host tree configuration. L. pulmonaria distribution was highly dependent on habitat quality for successful establishment, i.e., tree species identity, tree diameter, and several forest stand structure surrogates. For beech trees, tree diameter was the main factor influencing presence and cover of the lichen, although larger lichen-colonized trees were located close to focal trees, i.e., young trees. However, oak diameter was not an important factor, suggesting that bark roughness at all diameters favoured lichen establishment. Our results indicate that L. pulmonaria dispersal is not spatially restricted, but it is dependent on habitat quality. Furthermore, new spatial analysis tools suggested that L. pulmonaria cover exhibits a distinct pattern, although the spatial pattern of tree position and size was random.

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There is an increasing interest in understanding the role of epigenetic variability in forest species and how it may contribute to their rapid adaptation to changing environments. In this study we have conducted a genome-wide analysis of cytosine methylation pattern in Pinus pinea, a species characterized by very low levels of genetic variation and a remarkable degree of phenotypic plasticity. DNA methylation profiles of different vegetatively propagated trees from representative natural Spanish populations of P. pinea were analyzed with the Methylation Sensitive Amplified Polymorphism (MSAP) technique. A high degree of cytosine methylation was detected (64.36% of all scored DNA fragments). Furthermore, high levels of epigenetic variation were observed among the studied individuals. This high epigenetic variation found in P. pinea contrasted with the lack of genetic variation based on Amplified Fragment Length Polymorphism (AFLP) data. In this manner, variable epigenetic markers clearly discriminate individuals and differentiates two well represented populations while the lack of genetic variation revealed with the AFLP markers fail to differentiate at both, individual or population levels. In addition, the use of different replicated trees allowed identifying common polymorphic methylation sensitive MSAP markers among replicates of a given propagated tree. This set of MSAPs allowed discrimination of the 70% of the analyzed trees.