Tropical ecosystems play a key role in many aspects of Earth system dynamics currently of global concern, including carbon sequestration and biodiversity. To accurately understand complex tropical systems it is necessary to parameterise key ecological aspects, such as rates of change (RoC), species turnover, dynamism, resilience, or stability. To obtain a long-term (>50 years) perspective on these ecological aspects we must turn to the fossil record. However, compared to temperate zones, collecting continuous sedimentary archives in the lowland tropics is often difficult due to the active landscape processes, with potentially frequent volcanic, tectonic, and/or fluvial events confounding sediment deposition, preservation, and recovery. Consequently, the nature, and drivers, of vegetation dynamics during the last glacial are barely known from many non-montane tropical landscapes. One of the first lowland Amazonian locations from which palaeoecological data were obtained was an outcrop near Mera (Ecuador). Mera was discovered, and analysed, by Paul Colinvaux in the 1980s, but his interpretation of the data as indicative of a forested glacial period were criticised based on the ecology and age control. Here we present new palaeoecological data from a lake located less than 10 km away from Mera. Sediment cores raised from Laguna Pindo (1250 masl; 1°27′S, 78°05′W) have been shown to span the late last glacial period [50–13 cal kyr BP (calibrated kiloyears before present)]. The palaeoecological information obtained from Laguna Pindo indicate that the region was characterised by a relatively stable plant community, formed by taxa nowadays common at both mid and high elevations. Miconia was the dominant taxon until around 30 cal kyr BP, when it was replaced by Hedyosmum, Asteraceae and Ilex among other taxa. Heat intolerant taxa including Podocarpus, Alnus, and Myrica peaked around the onset of the Last Glacial Maximum (c. 21 cal kyr BP). The results obtained from Laguna Pindo support Colinvaux’s hypothesis that glacial cooling resulted in a reshuffling of taxa in the region but did not lead to a loss of the forest structure. Wide tolerances of the plant species occurring to glacial temperature range and cloud formation have been suggested to explain Pindo forest stability. This scenario is radically different than the present situation, so vulnerability of the tropical pre-montane forest is highlighted to be increased in the next decades.
El presente proyecto se ejecutó en la “Estación Biológica Pindo Mirador” gracias al financiamiento de la Universidad Tecnológica Equinoccial (UTE). La zona de estudio constituyó los bosques de la Estación; se consideró como variable la pendiente del terreno. El diseño utilizado fue el muestreo en fajas que permitió captar mejor la variación de la población, debido a la heterogeneidad en su composición florística. El tamaño de cada parcela fue de 200 X 50 metros, lo que representa 1Ha; la intensidad de muestreo fue del 5%. Además se trabajó con subparcelas circulares para inventariar la regeneración natural de las especies. Los resultados evidencian especies forestales de uso maderable y no maderable. Se propone considerar al bosque como un sistema biológico con usos múltiples: valor ambiental, ecológico, recreativo; así como un lineamiento general la regeneración natural como proceso natural que mantiene al bosque. Este inventario servirá de punto de partida para establecer estrategias de manejo del bosque y como un estudio que puntualiza la importancia de la Declaratoria de Bosque Protector a la zona de estudio de la Estación Biológica Pindo Mirador.
El presente estudio se realizó en la Estación Biológica Pindo Mirador con el objetivo de identificar las especies de flora en diferentes áreas de acuerdo a la gradiente altitudinal. Los bosques de la Estación Biológica Pindo Mirador son ecosistemas de la Amazonía donde habitan una variedad de especies; se trabajó con transectos radiales de tal forma que esta metodología permitió cubrir un mayor número de especies. Los datos obtenidos fueron analizados y se estableció la composición florística, índice de diversidad, índice de similitud y el estado de conservación de las especies de bosque primario y secundario. La densidad fue mayor en los bosques secundarios, mientras la diversidad de acuerdo al índice obtenido es medianamente baja, siendo la similitud entre los transectos establecidos más similar a los 1300 metros. Los bosques secundarios se encuentran en un estado de recuperación.
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