RESUMO

Changes in global and regional precipitation regimes are among the most pervasive components of climate change. Intensification of rainfall cycles, ranging from frequent downpours to severe droughts, could cause widespread, but largely unknown, alterations to trophic structure and ecosystem function. We conducted multi-site coordinated experiments to show how variation in the quantity and evenness of rainfall modulates trophic structure in 210 natural freshwater microcosms (tank bromeliads) across Central and South America (18°N to 29°S). The biomass of smaller organisms (detritivores) was higher under more stable hydrological conditions. Conversely, the biomass of predators was highest when rainfall was uneven, resulting in top-heavy biomass pyramids. These results illustrate how extremes of precipitation, resulting in localized droughts or flooding, can erode the base of freshwater food webs, with negative implications for the stability of trophic dynamics.

Assuntos

RESUMO

In several tropical and subtropical forests, plants of the understorey act as an ecological filter that differentially affects woody species regeneration. In convex sectors of the Schinopsis balansae (Anacardiaceae) forests of the Southeastern Chaco there are dense colonies of terrestrial bromeliads. These may influence forest regeneration by intercepting rain water and propagules in their tanks. Within colonies, the spatial distribution of bromeliads is clumped because their clonal growth leaves numerous internal gaps. In this study we describe the internal heterogeneity of three bromeliad colonies (plots) and analyze how this heterogeneity affects Acacia praecox regeneration (i.e. seedling recruitment and survival). In January 1996, we randomly placed three transects with 150 contiguous quadrats of 100 cm2 in each plot. For each quadrat we recorded the type of floor cover (i.e. bromeliads, herbs, litter, or bare soil) and the presence of A. praecox seeds or seedlings. In July 1996 we relocated the transects and recorded seedling survival. Bromeliad colonies showed a high internal heterogeneity. Almost half of the 450 quadrats were covered by two terrestrial bromeliads. Aechmea distichantha was recorded in 81% of all quadrats with bromeliads, and Bromelia serra in the others. All quadrats with bromeliads were covered by litter. Half of them were occupied by the bases of bromeliads and the others were covered by their leaves. In contrast, where bromeliads were not present, soil surface was covered by litter in 83% and by herbaceous vegetation in 11% of the quadrats; very few quadrats were covered by bare soil. In January 1996, we recorded 127 seeds and 176 seedlings of A. praecox. Seed and seedling densities of A. praecox were similar in quadrats with and without bromeliads, but variability in seedling density of A. praecox was higher within than among plots. Seed density was higher in quadrats covered by bromeliad leaves than inside the tanks.

En varios bosques tropicales y subtropicales, las plantas del sotobosque actúan como filtro ecológico que afecta diferencialmente la regeneración de las especies leñosas. En los bosques de Schinopsis balansae (Anacardiaceae) del Chaco Oriental existen densas colonias de bromeliáceas terrestres que afectarían su regeneración al interceptar el agua de lluvia y los propágulos dentro de sus tanques. Estas bromeliáceas tienen distribución agrupada dejando espacios libres entre ellas. Describimos la heterogeneidad de tres colonias y analizamos como afectan la regeneración de Acacia praecox. En enero 1996, colocamos en cada colonia tres transectos con 150 parcelas de 100 cm2. En cada parcela registramos el tipo de cobertura (i.e. bromeliáceas, hierbas, hojarasca ó suelo desnudo) y la presencia de semillas o plántulas de A. praecox. En julio 1996, registramos la supervivencia de plántulas. Las colonias de bromiliáceas mostraron una alta heterogeneidad interna. Casi la mitad de las 450 parcelas estuvo cubierto por dos bromeliáceas terrestres. Aechmea distichantha se registró en 81% de las parcelas con bromeliáceas y Bromelia serra en las otras. Todas las parcelas estuvieron cubiertas por hojarasca. La mitad de ellas estuvieron cubiertas por hojas de bromeliáceas y el resto ocupado por sus bases. Donde no había bromeliáceas, el suelo estuvo cubierto por mantillo (83%), herbáceas (11%), u otros. En enero registramos 127 semillas y 176 plántulas de A. praecox. La densidad de ambas fue similar en parcelas con y sin bromeliáceas, pero su variabilidad fue mayor dentro de cada colonia que entre ellas. La densidad de semillas fue mayor debajo de las hojas de bromeliáceas que dentro de las plantas. La supervivencia de plántulas fue superior en parcela con bromeliáceas en sólo una de las tres colonias. Ninguna plántula sobrevivió dentro de las bromeliáceas. Aparentemente...

Assuntos

RESUMO

In several tropical and subtropical forests, plants of the understorey act as an ecological filter that differentially affects woody species regeneration. In convex sectors of the Schinopsis balansae (Anacardiaceae) forests of the Southeastern Chaco there are dense colonies of terrestrial bromeliads. These may influence forest regeneration by intercepting rain water and propagules in their tanks. Within colonies, the spatial distribution of bromeliads is clumped because their clonal growth leaves numerous internal gaps. In this study we describe the internal heterogeneity of three bromeliad colonies (plots) and analyze how this heterogeneity affects Acacia praecox regeneration (i.e. seedling recruitment and survival). In January 1996, we randomly placed three transects with 150 contiguous quadrats of 100 cm(2) in each plot. For each quadrat we recorded the type of floor cover (i.e. bromeliads, herbs, litter, or bare soil) and the presence of A. praecox seeds or seedlings. In July 1996 we relocated the transects and recorded seedling survival. Bromeliad colonies showed a high internal heterogeneity. Almost half of the 450 quadrats were covered by two terrestrial bromeliads. Aechmea distichantha was recorded in 81% of all quadrats with bromeliads, and Bromelia serra in the others. All quadrats with bromeliads were covered by litter. Half of them were occupied by the bases of bromeliads and the others were covered by their leaves. In contrast, where bromeliads were not present, soil surface was covered by litter in 83% and by herbaceous vegetation in 11% of the quadrats; very few quadrats were covered by bare soil. In January 1996, we recorded 127 seeds and 176 seedlings of A. praecox. Seed and seedling densities of A. praecox were similar in quadrats with and without bromeliads, but variability in seedling density of A. praecox was higher within than among plots. Seed density was higher in quadrats covered by bromeliad leaves than inside the tanks. Seedling survival of A. praecox was slightly higher in quadrats with bromeliads in only one of the three plots. No seedling survived inside the bromeliad tanks. Apparently. bromeliad colonies have no effect on seedling regeneration of A. praecox.

Assuntos