918 resultados para mangrove snapper
Resumo:
The anisotropy of the Biscayne Aquifer which serves as the source of potable water for Miami-Dade County was investigated by applying geophysical methods. Electrical resistivity imaging, self potential and ground penetration radar techniques were employed in both regional and site specific studies. In the regional study, electrical anisotropy and resistivity variation with depth were investigated with azimuthal square array measurements at 13 sites. The observed coefficient of electrical anisotropy ranged from 1.01 to 1.36. The general direction of measured anisotropy is uniform for most sites and trends W-E or SE-NW irrespective of depth. Measured electrical properties were used to estimate anisotropic component of the secondary porosity and hydraulic anisotropy which ranged from 1 to 11% and 1.18 to 2.83 respectively. 1-D sounding analysis was used to models the variation of formation resistivity with depth. Resistivities decreased from NW (close to the margins of the everglades) to SE on the shores of Biscayne Bay. Porosity calculated from Archie's law, ranged from 18 to 61% with higher values found along the ridge. Higher anisotropy, porosities and hydraulic conductivities were on the Atlantic Coastal Ridge and lower values at low lying areas west of the ridge. The cause of higher anisotropy and porosity is attributed to higher dissolution rates of the oolitic facies of the Miami Formation composing the ridge. The direction of minimum resistivity from this study is similar to the predevelopment groundwater flow direction indicated in published modeling studies. Detailed investigations were carried out to evaluate higher anisotropy at West Perrine Park located on the ridge and Snapper Creek Municipal well field where the anisotropy trend changes with depth. The higher anisotropy is attributed to the presence of solution cavities oriented in the E-SE direction on the ridge. Similarly, the change in hydraulic anisotropy at the well field might be related to solution cavities, the surface canal and groundwater extraction wells.
Resumo:
Diamondback terrapins (Malaclemys terrapin) are native to the remote oceanic islands of Bermuda and presently inhabit only four small brackish water ponds on a private golf course. The life history of this species is poorly understood on Bermuda and so the aim of this study was to fill these knowledge gaps, to compare the results with what is known from other areas in the North American range, and to inform the development of a local management plan. The results of a mark-recapture census revealed that ca. 100 individuals ≥81 mm straight carapace length live on Bermuda, of which nearly half (48.5%) were considered sexually mature. The population is dominated by females (sex ratio 2.9:1) and annual recruitment over the three year period was found to be extremely low (approximately two terrapins). Female diamondback terrapins in Bermuda nest almost exclusively within a limited number of sand bunkers on the golf course. Nesting commenced in late March or early April and ended in late August. Peak oviposition was observed in May and June. Clutch size averaged 5.1 eggs (range 0-10; SD 2.4) and the incubation period averaged 61.8 days (range 49-83; SD 10.5). Delayed emergence was documented, with 43.8% of the hatchlings remaining in their natal nests over the winter months. The mean annual hatching success rate was determined to be 19% (range 17.6-21; SD 1.9). Radio-telemetry was used to investigate the movements and survivorship of postemergent hatchling diamondback terrapins. The results indicated that mangrove swamps and grass-dominated marshes adjacent to the ponds are important developmental habitats for hatchlings. Yellow-crowned night herons (Nyctanassa violacea) were found to be significant predators of small terrapins during spring emergence. Small aquatic gastropods comprised 66.7% of the faecal samples analysed from the Bermudian population. Scavenged fish and vertebrate animal remains, terrestrial arthropods, polychaete worms and bivalves were consumed in lesser amounts. Sediment from the pond environment was found in 74% of the faecal samples analysed and is believed to have been incidentally ingested while foraging for the small benthic gastropods. Eco-toxicological analyses of the pond sediment, prey and terrapin eggs showed that the Bermudian diamondback terrapins live and feed in wetland habitats characterised by chronic, multifactorial contamination; principally total petroleum hydrocarbons, polycyclic aromatic hydrocarbons and a variety of heavy metals. This study found that some of those contaminants are accumulating in the gastropod prey as well as being transferred to terrapin eggs. This may be reducing the incidence of successful embryonic development for this species in Bermuda and may likely contribute to the observed low hatching rates. These collective findings indicate that the Bermudian population is very vulnerable to local extirpation.
Resumo:
La microcuenca del río Poás (ubicada entre el volcán Barva y el volcán Poás, hasta la confluencia con el río Grande cerca de la ciudad de Alajuela) posee un alto potencial para la formación de acuíferos de alta calidad. Por este motivo sus recursos naturales deben utilizarse adecuadamente. La mejor manera de lograr lo anterior es mediante la planificación del uso de la tierra. En esta investigación se plantea para ello el ordenamiento territorial y el manejo de cuencas. Para este propósito se realiza una zonificación mediante la cual se identifican las siguientes zonas: sin restricción de uso, uso restringido y uso muy restringido. La mayor parte de la m icrocuenca (64,6%) se encuentra en la categoría de “sin restricción de uso”. Sin embargo. se hace necesaria la intervención con rapidez en sectores ubicados en la parte alta de la microcuenca que se clasifican de “uso muy restringido”. En relación con el recurso hídrico, en la microcuenca en los últimos 14 años y de acuerdo con la metodología aplicada, se ha elevado la producción hídrica, específicamente en la escorrentía y la ganancia. En general aumentó en 1,6%.Abstract:The Poas river micro watershed (located between the Barva and Poas volcanoes reaching the confluence of the Grande river near the city of Alajuela) has high potential for developing high quality aquifers, thus, its natural resnurces should be utilized adequately. This is best done by proper land use planning. In this study guidelines are presented for land use planning and watershed management. Land use is zoned or classified for the following uses:unrestricted use, restricted use, and highly restricted use. Most of the micro watershed (64.6 percent) is classified or zoned as ‘unrestricted use.’ However, urgent intervention is needed in demand and the possibility to export it. However, it is also possible to see the negative impaci of the project, such as: indigenous territories and a pan of the Interamerican Road being flooding, population displacement and the environmental ¡mpact on the Terraba-Sierpe mangrove. This diversity and incompatibility of factors and interest make a complex scenario that potentializes diverse conflicts.