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  1. Using Remote Sensing to Reassess the Mass Mortality of Diadema antillarum 1983-1984: Conservation Biology, Vol. 15, No. 4. (2001), pp. 885-891.The 1983-1984 mass mortality of the sea urchin Diadema antillarum remains one of the most severe die-offs ever recorded in the Caribbean. Before 1983, the herbivore D. antillarum was pervasive on coral reefs in the region. Nine months after first detection of the mass mortality, 95% of the urchins had perished, and algal cover of coral increased between 100% and 250%. A water-borne pathogen was hypothesized as the causative agent, but it was never isolated. To date, surface current patterns have been used exclusively to explain both the cause and the distribution patterns of the mortality event. Using archived satellite images, we re-examined the water-borne pathogen hypothesis and investigated whether other mechanisms could also account for the dissemination pattern in some areas. In addition, archived satellite images were utilized to detect changes in coral reef reflectance. For infections in the Gulf of Mexico and Bermuda, satellite images confirm that surface currents are likely responsible for the distribution of the pathogen. For infections in the eastern Caribbean (Curacao, U.S. Virgin Islands, Barbados), however, another mechanism, possibly ballast water exchange, must be considered because the surface current and infection patterns do not coincide. Changes in coral reflectance were detectable from Landsat thermatic mapping data before and after the mass mortality and correspond to the change in algal cover. Results from our study demonstrate the potential of satellite images for use in determining connectivity between regions of the Caribbean and in detecting changes in coral reef cover. Utilizacion de Percepcion Remota para Reanalizar la Mortandad Masiva de Diadema antillarum de 1983-1984 Resumen: El evento de mortandad masiva de 1983-1984 del erizo de mar Diadema antillarum se mantiene como uno de los eventos de mortandad masiva mas severos de que se tengan registros en el Caribe. Antes de 1983, el herviboro D. antillarum, abundaba en los arrecifes de coral de la region. Nueve meses despues de la deteccion de la mortandad masiva, 95% de los erizos fallecieron y la cobertura de algas sobre el coral se incremento entre 100 y 250%. Se establecio la hipotesis de que el agente causante fue un patogeno de origen acuatico, pero nunca fue aislado. A la fecha, los patrones de corrientes superficiales han sido usados exclusivamente para explicar tanto el agente causal como los patrones de distribucion de la mortandad. Utilizando imagenes de archivo de satelite, re-examinamos la hipotesis del agente de origen acuatico e investigamos si otros mecanismos podrian tambien ser considerados en los patrones de diseminacion de algunas areas. Para infecciones del Golfo de Mexico y Bermudas, las imagenes de satelite confirman que las corrientes superficiales son los responsables mas probables de la distribucion del patogeno. Sin embargo, para infecciones en el Este del Caribe (Curacao, U.S., Islas Virginia, Barbados), otro mecanismo, posiblemente el cambio de agua de lastre, podria ser considerado debido a que las corrientes superficiales y los patrones de infeccion no coinciden. Se detectaron cambios en la reflectancia del coral por medio de datos del mapeador tematico Landsat antes y despues de la mortandad masiva, mismos que correspondiero n con los cambios en la cobertura algal. Los resultados de nuestro estudio demuestran el potencial de usar imagenes de satelite para determinar la conectividad entre regiones del Caribe y para detectar cambios en la cobertura del arrecife coralino.

    Source: Conservation Biology, Vol. 15, No. 4. (2001), pp. 885-891.

  2. Man's Role in Changing the Face of the Ocean: Biological Invasions and Implications for Conservation of Near-Shore Environments: Conservation Biology, Vol. 3, No. 3. (1989), pp. 265-273.Human activities, primarily the global movement of organisms associated with ocean-going vessels and with commercial fishery products, have lead to the redistribution of a vast number of marine organisms over the past five centuries. Most biological surveys postdated these transport events, so the distribution of many of these now cosmopolitan species has been interpreted as the result of natural processes, leading to underestimates of the role of humans in altering patterns of natural diversity and distribution of marine organisms along the coastal margins of the world Perceptions of the natural state of some systems versus their recent ecological alteration are illustrated by the National Estuarine Reserve Research System, within which many "natural" sanctuaries have been highly altered by exotic species The modern scale and rate of new human-mediated invasions in the ocean are difficult to recognize due to the lack of communication among scientists working with different groups of organisms, different habitats, and different regions. Available evidence suggests that introductions continue unabated on a large scale throughout the world Despite the existence since 1973 of a number of international conventions to control the movement of exotic marine organisms adequate control still occurs largely at the regional and local levels. La reorganizacion de una gran cantidad de organismos marinos en los Sultimos 5 siglos se debe a actividades humanus, especialmente a desplazamiento s globales de organismos asociados con embarcaciones marinus y con productos pesqueros comerciales La mayoria de encuestas biologicas posfechan dichos eventos de transportacion , y por consecuencia se intetpreta la distribucion de muchas de estas especies, hoy cosmopolitas, como resultado de pcesos naturales, subestimando el rol humano en la alteracion de la diversidad natural y en la distribucion de organismos marinos en los margenes costeros del mundo. Se ilustran percepciones sobre el estado natural de algunos sistemas versus su reciente alteracion ecologica en el "NATIONAL ESTUARINE RESERVE RESEARCH SYSTEM," dentro del cual muchos santuarios "naturales" han sido fuertemente alterados por especies exoticas Debido a la falta de comunicacion entre los cientificos que trabajan con diferentes grupos de organismos, habitats y regiones, es drficil reconocer la escala y tasa de las invasiones recientes en los oceanos, causados por actividades humanas. Evidencias disponibles sugieren que las introducciones continuan en gran escala en todo el mundo. A pesar que desde 1973 se han establecido numerosas convenciones internacionale s con el motivo de controlar el desplazamiento de otganismos exoticos marinos, un control adecuado solo ocurre en los niveles locales y regionales.

    Source: Conservation Biology, Vol. 3, No. 3. (1989), pp. 265-273.

  3. Conservation of Marine and Coastal Biodiversity in Brazil: Conservation Biology, Vol. 19, No. 3. (June 2005), pp. 625-631.

    Source: Conservation Biology, Vol. 19, No. 3. (June 2005), pp. 625-631.

  4. Coastal Ecosystem-Base d Management with Nonlinear Ecological Functions and Values: Science, Vol. 319, No. 5861. (18 January 2008), pp. 321-323.A common assumption is that ecosystem services respond linearly to changes in habitat size. This assumption leads frequently to an "all or none" choice of either preserving coastal habitats or converting them to human use. However, our survey of wave attenuation data from field studies of mangroves, salt marshes, seagrass beds, nearshore coral reefs, and sand dunes reveals that these relationships are rarely linear. By incorporating nonlinear wave attenuation in estimating coastal protection values of mangroves in Thailand, we show that the optimal land use option may instead be the integration of development and conservation consistent with ecosystem-base d management goals. This result suggests that reconciling competing demands on coastal habitats should not always result in stark preservation-v ersus-conversi on choices. 10.1126/scienc e.1150349

    Source: Science, Vol. 319, No. 5861. (18 January 2008), pp. 321-323.

  5. Significant contribution of the 18.6 year tidal cycle to regional coastal changes: Nature Geosci, Vol. 1, No. 3. (March 2008), pp. 169-172.

    Source: Nature Geosci, Vol. 1, No. 3. (March 2008), pp. 169-172.

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