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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0034-77442005000300001</article-id>
<title-group>
<article-title xml:lang="en">31ST Scientific Meeting of the Association of Marine Laboratories of the Caribbean (AMLC)</article-title>
<article-title xml:lang="es">31ª Reunión Científica de la Asociación de Laboratorios Marinos del Caribe (ALMC)</article-title>
</title-group>
<aff id="A">
<institution>,  </institution>
<addr-line> </addr-line>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
</pub-date>
<volume>53</volume>
<fpage>xiii</fpage>
<lpage>xiv</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300001&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300001&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300001&amp;lng=en&amp;nrm=iso"></self-uri></article-meta>
</front>
</article>
<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance">
<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0034-77442005000300002</article-id>
<title-group>
<article-title xml:lang="en">Welcome</article-title>
<article-title xml:lang="es">Bienvenida</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>LeGore</surname>
<given-names>Steve</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution>,Executive Director  </institution>
<addr-line> </addr-line>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
</pub-date>
<volume>53</volume>
<fpage>xv</fpage>
<lpage>xv</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300002&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300002&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300002&amp;lng=en&amp;nrm=iso"></self-uri></article-meta>
</front>
</article>
<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance">
<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0034-77442005000300003</article-id>
<title-group>
<article-title xml:lang="en">Schedule of Oral Presentations</article-title>
<article-title xml:lang="es">Programa de Presentaciones Orales</article-title>
</title-group>
<aff id="A">
<institution>,  </institution>
<addr-line> </addr-line>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
</pub-date>
<volume>53</volume>
<fpage>xvii</fpage>
<lpage>xxii</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300003&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300003&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300003&amp;lng=en&amp;nrm=iso"></self-uri></article-meta>
</front>
</article>
<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance">
<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0034-77442005000300004</article-id>
<title-group>
<article-title xml:lang="en">Poster Presentations</article-title>
<article-title xml:lang="es">Presentaciones en Cartel</article-title>
</title-group>
<aff id="A">
<institution>,  </institution>
<addr-line> </addr-line>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
</pub-date>
<volume>53</volume>
<fpage>xxiii</fpage>
<lpage>xxv</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300004&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300004&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300004&amp;lng=en&amp;nrm=iso"></self-uri></article-meta>
</front>
</article>
<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance">
<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0034-77442005000300005</article-id>
<title-group>
<article-title xml:lang="en">Development and field application of a molecular probe for the primary pathogen of the coral disease white plague type II</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Richardson</surname>
<given-names>Laurie L</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Mills</surname>
<given-names>DeEtta K</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Remily</surname>
<given-names>Elizabeth R</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Voss</surname>
<given-names>Joshua D</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution>,Florida International University  </institution>
<addr-line>Miami Florida</addr-line>
<country>USA</country>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
</pub-date>
<volume>53</volume>
<fpage>1</fpage>
<lpage>10</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300005&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300005&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300005&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>One of the current problems in the field of coral disease research is that of tracking coral pathogens in the natural environment.A promising method to do this is by use of pathogen-specific molecular probes. However,this approach has been little used to date.We constructed,and validated in the laboratory,a fluoro-chrome-labeled molecular probe specific to Aurantimonas coralicida ,the bacterial pathogen of the Caribbean coral disease white plague type II (WPII).We then used the probe to test field samples of diseased coral tissue for the presence of this pathogen.Probe design was based on a unique subset (25 nucleotides)of the complete16S rRNA gene sequence derived from a pure culture of the pathogen.The pathogen-specific probe was labeled with the fluorochrome GreenStar*&amp;trade;FITC (fluorescein isothiocyanate,GeneDetect Ltd,New Zealand).As a control, we used the universal eubacterial probe EUB 338,labeled with a different fluorochrome (TRITC,tetra-methyl-rhodamine isothiocyanate).Both probes were applied to laboratory samples of pure cultures of bacteria, and field samples collected from the surface of the disease line of corals exhibiting signs of white plague (types I and II),healthy controls,and corals with an uncharacterized disease (&quot;patchy necrosis &quot;).All samples were analyzed using fluorescence in situ hybridization (FISH).We have determined that the probe is specific to our laboratory culture of the coral pathogen,and does not react with other bacterial species (the eubacterial probe does).The WPII pathogen was detected in association with diseased coral samples collected from coral colonies on reefs of the Bahamas (n=9 samples)exhibiting signs of both WPI and WPII.Diseased (and healthy)tissue samples (n=4)from corals exhibiting signs of &quot;patchy necrosis &quot;were also assayed.In this case the results were negative, indicating that the same pathogen is not involved in the two diseases.Incorporation and use of pathogen-specific probes can significantly expand our knowledge of the etiology of coral diseases.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Uno de los problemas actuales en el campo de la investigación sobre las enfermedades de corales es el de poder seguir a los patógenos en el ambiente natural.Un método prometedor para lograrlo es el uso de sondas moleculares específicas para el patógeno.Sin embargo,esta técnica ha sido poco usada hasta la fecha.Construimos y validamos en el laboratorio una sonda molecular de fluorocromo marcado específicamente para Aurantimonas coralicida ,la bacteria responsable de la enfermedad de corales del Caribe,plaga blanca Tipo II (PBII).Después usamos la sonda con muestras de campo de tejidos de corales enfermos para detectar la presencia del patógeno.La sonda se diseñó usando un sub-grupo único de 25 nucleótidos del gen 16S del rARN derivado de cultivos puros del patógeno.La sonda específica para el patógeno se marcó con fluorocromo GreenStar*&amp;trade; FITC (fluorescein isotiocianato,GeneDetect Ltd,New Zealand).Como testigo usamos la sonda universal de eubacterias EUB 338,marcada con un fluorocromo diferente (TRITC,tetra-metil-rodamina isotiocianato).Ambas sondas fueron usadas con muestras de laboratorio de cultivos puros de bacterias,y muestras de campo recolectadas de la superficie de la línea de la enfermedad en corales con signos de plaga blanca (tipos I y II),de corales sanos y de corales con enfermedades no características (parches de tejido necrótico).Todas las muestras fueron analizadas usando hibridización fluorescente in situ .Determinamos que la sonda es específica para el patógeno cultivado en nuestro laboratorio y no reacciona con otras especies de bacterias (la sonda para eubacterias sí).El patógeno de PBII fue detectado en muestras de corales enfermos (exhibían signos de PBI y PBII)recolectadas en arrecifes de Bahamas (n=9 muestras).Muestras de tejidos enfermos (y sanos)(n=4)de corales con parches necróticos fueron probados.En este caso los resultados fueron negativos,indicando que el mismo patógeno no es responsable de las dos enfermedades.El desarrollo y uso de sondas específicas para cierto patógeno puede ampliar significativamente nuestro conocimiento de la etiología de enfermedades de corales.</p></abstract>
<kwd-group>
<kwd>White plague</kwd>
<kwd>coral pathogen</kwd>
<kwd>Aurantimonas coralicida</kwd>
<kwd>coral diseases</kwd>
<kwd>pathogen specific molecular probe</kwd>
<kwd>Plaga blanca</kwd>
<kwd>patología de corales</kwd>
<kwd>Aurantimonas coralicida</kwd>
<kwd>enfermedades de coral</kwd>
<kwd>sonda molecular para patógeno específico</kwd>
</kwd-group>
</article-meta>
</front>
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<journal-title>Revista de Biología Tropical</journal-title>
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<institution>,Institute of Marine Affairs  </institution>
<addr-line>Trinidad </addr-line>
<country>West Indies</country>
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<fpage>11</fpage>
<lpage>23</lpage>
<copyright-statement/>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300006&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300006&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300006&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The Godineau (South Oropuche)Swamp (3171 ha)on the southwestern coast of Trinidad (10 º13- 15 ’N,61 º30-32 ’W)is heavily impacted by anthropogenic activities including fishing,oil exploration, drainage manipulation and wetland clearance.To reduce the negative effects of these activities and to manage the swamp more sustainably,more quantitative information is needed on the ecology of the wetland and the activities that occur within it.This study focuses on the distribution of the fish resources and exploited fisheries as a basis for more informed management directives. Sampling was conducted during 2002,in April-May (for dry season)and July-September (for wet season sampling).Ichthyofauna was sampled both day and night using trammel nets and a push seine.Fishing activities were assessed using a questionnaire and informal discussions with fishers.The wetland supports over 29 species of fish distributed over the freshwater,estuarine and saline zones (n=1454). Species distribution is seasonal,with evidence of the wetland being used as a spawning ground. Species richness and species diversity (Shannon-Weiner Index)for the wetland ranged over 2-11 and 0.162-0.967,respectively, in the dry season and 2-7 and 0.036-0.903,respectively,in the wet season.Communities inhabiting the saline and estuarine zones of the wetland were dominated by a single species,Hexanematichthys bonillai .Percent Similarity Indices were 41.8%for freshwater, 72.7%for estuarine and 79.8%for estuarine-saline communities. The commercial species accounted for 18%of total catch sampled and consisted of Centropomus undecimalis, Megalops atlanticus ,Hoplosternum littorale ,Hoplias malabaricus ,Ophioscion punctatissimus and Macrodon ancyclodon .Full-time and part-time fishers,including recreational fishers,accounted for 14.3%and 85.7%, respectively of all fishers surveyed (n=56).A conservative estimate of the revenue earned directly at point of sale for fish and shellfish,is approximately US$43 000 per annum.Fishing is important in the area.Management directives taking into account the ecology of the target organisms are needed to allow these fishing practices to be continued in a sustainable manner.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El pantano Godineau (Oropuche Sur)(3171 ha)en la costa suroeste de Trinidad (10 º13-15 ’N,61 º30-32 ’W), sufre un impacto fuerte por actividades antropogénicas como pesca,exploración petrolera, drenaje y destrucción del humedal.Para reducir los efectos negativos de las actividades y dar un manejo sostenible,se necesita más información cuantitativa sobre la ecología de este lugar y las actividades que en él se llevan a cabo.Este estudio se enfoca en la distribución de los peces y de las pesquerías, como información base para el manejo.El muestreo fue realizado en el 2002,en abril y mayo (para la época seca) y de julio a septiembre (para la época lluviosa).Se muestreó ictiofauna de día y de noche con redes de trasmallo y redes de empuje (chinchorro).Las actividades pesqueras fueron cuantificadas utilizando un cuestionario y discusiones informales con los pescadores.El humedal mantiene más de 29 especies de peces distribuidas en ambientes de agua dulce,estuarinos y de agua salada (n=1454).La distribución de las especies es estacional,y hay evidencia de que el pantano es utilizado como área de desove.La riqueza de especies y la diversidad (índice de Shannon-Weiner)para el humedal,tienen un ámbito de 2-11 y 0.162-0.967,respectivamente,en la estación seca y de 2-7 y 0.036-0.903,respectivamente,en la estación lluviosa. Hexanematichthys bonillai fue la especie dominante en las comunidades que habitan zonas de agua salada y estuarinas del humedal.Los porcentajes del índice de similitud fueron del 41.8%para agua dulce,72.7%para estuarios y 79.8% para comunidades estuarinas-saladas.Las especies comerciales comprendieron el 18%de la captura total y constan de:Centropomus undecimalis,Megalops atlanticus, Hoplosternum littorale,Hoplias malabaricus,Ophioscion punctatissimus y Macrodon ancyclodon .Los pescadores de tiempo completo y tiempo parcial,incluyendo los pescadores recreativos,fueron el 14.3%y 85.7%respectivamente,de todos los pescadores encuestados (n=56).Una estimación conservadora de las ganancias por peces y otros mariscos,directamente en el punto de venta,es de aproximadamente US$43 000 por año.La pesca es importante en el área.Se necesitan directrices de manejo que tomen en cuenta la ecología de los organismos clave,para permitir estas prácticas pesqueras de una manera sostenible.</p></abstract>
<kwd-group>
<kwd>Wetland fisheries</kwd>
<kwd>wetland ichthyofauna</kwd>
<kwd>seasonal distribution</kwd>
<kwd>island fisheries</kwd>
<kwd>Caribbean fresh- water fisheries</kwd>
<kwd>Pesquería en humedales</kwd>
<kwd>ictiofauna de humedales</kwd>
<kwd>distribución estacional</kwd>
<kwd>pesquería en islas</kwd>
<kwd>pesquería de agua dulce en el Caribe</kwd>
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<addr-line>Lajas </addr-line>
<country>Puerto Rico</country>
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<fpage>25</fpage>
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<copyright-statement/>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300007&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300007&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300007&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Studies of temporal and spatial changes in phytoplankton biomass and turbidity provide essential information on coral reef ecosystem function and health.Fluctuation of phytoplankton biomass responds to several factors including nutrient inputs,both anthropogenic and natural,while turbidity is mostly affected by sediment resuspension or transport from terrestrial systems.These parameters can be used as sentinels of significant environmental factors &quot;modifying &quot;coral reef systems.A chlorophyll a concentration (Chl a )and turbidity (Turb)in situ logger was installed at 10 stations from June 4 to July 7,2003 in La Parguera Natural Reserve (Southwestern Puerto Rico)to assess short-term temporal and geographic variation in patterns of phytoplankton biomass and turbidity at pre-selected sites as part of an interdisciplinary long-term study.Average station Chl a variation was 0.17-1.12 µg l -1 and 0.2-23.4 NTU for Turb.Results indicate that the western near-coastal stations had higher levels of Turb and Chl a .The easternmost mid shelf station,Romero reef,was similar to coastal stations probably due to nutrient and suspended sediment inputs from a source external to our study area to the east,Guánica Bay.Comparisons between different sampling days indicate significant differences between days for most stations suggesting that one-time discrete sampling may not be representative of average water column conditions and illustrate the dynamic nature of coral reef systems.Further work is warranted to assess seasonal changes that integrate short-term (daily)variability in both Turb and Chl a .</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Los estudios sobre cambios temporales y espaciales de biomasa fitoplanctónica y de urbidad, proveen información esencial sobre la función y salud de los sistemas arrecifales.Fluctuaciones de la biomasa de fitoplancton responden a factores como entradas de nutrientes de fuentes antropogénicas y/o naturales,mientras que la turbidez responde mayormente a la resuspensión de sedimentos o la entrada de sedimentos de sistemas terrestres.Por tal motivo,estos parámetros pueden ser indicadores de factores ambientales que modifican los arrecifes coralinos.Un recolector in situ,de datos de concentración de clorofila a (Chl a )y turbidez (Turb),fue instalado en 10 estaciones del 4 de junio al 7 de julio del 2003 en la Reserva Natural de La Parguera (Suroeste de Puerto Rico)para establecer patrones geográficos y temporales de biomasa de fitoplancton y turbidez como parte de un estudio interdisciplinario. La variación promedio de Chl a por estación fue 0.17-1.12 µg l -1 mientras para Turb fue 0.2-23.4 NTU.Los resultados indican que las estaciones costeras al oeste tenían niveles mayores de Turb y Chl a mientras que las aguas de un arrecife en la plataforma intermedia al este,Romero, tenían características similares a las estaciones costeras. Esto se debe a la proximidad de Romero a una fuente de nutrientes y sedimentos suspendidos al este del área de estudio,la Bahía de Guánica.Se encontraron diferencias significativas para Chl a y Turb entre diferentes días de muestreo en la mayor parte las estaciones,lo que sugiere que muestreos discretos no son necesariamente representativos de las condiciones promedio de la columna de agua e ilustra lo dinámico de los sistemas arrecifales.Se necesita trabajo que integre la variabilidad a corto plazo (diaria)en el estimado estacional de Chl a y Turb.</p></abstract>
<kwd-group>
<kwd>Water quality</kwd>
<kwd>coral reef</kwd>
<kwd>turbidity</kwd>
<kwd>chlorophyll a</kwd>
<kwd>in situ monitoring</kwd>
<kwd>Calidad de agua</kwd>
<kwd>arrecife coralino</kwd>
<kwd>turbidez</kwd>
<kwd>clorofila a</kwd>
<kwd>monitoreo in situ</kwd>
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<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
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</journal-meta>
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<article-id>S0034-77442005000300008</article-id>
<title-group>
<article-title xml:lang="en">Spatial distribution of heavy metals in sediments from the Gulf of Paria,Trinidad</article-title>
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<institution>,Institute of Marine Affairs  </institution>
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<pub-date pub-type="pub">
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<pub-date pub-type="epub">
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<volume>53</volume>
<fpage>33</fpage>
<lpage>40</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300008&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300008&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300008&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The Gulf of Paria receives heavy metal input from urban runoff,industrial and agricultural activity, sewage and domestic wastes:both from the west coast and from inland areas of Trinidad.Non-residual concentrations of nine metals,as well as total mercury concentrations,were used to determine spatial distributions of heavy metals in sediments in the Gulf of Paria.Surficial sediment samples were collected at 37 stations,which included the mouths of 11 major rivers that flow into the Gulf of Paria.Stations were sampled twice during the wet season (July 1998 and November/December 1998)and twice during the dry season (March 1999 and April 1999).Sediments were analyzed for aluminium (Al),cadmium (Cd),chromium (Cr),copper (Cu),iron (Fe), lead (Pb),manganese (Mn),nickel (Ni),zinc (Zn)and mercury (Hg).Total Organic Carbon (TOC)and grain size analyses were also performed on the sediments.Principal component analysis showed that sediments from river mouths subject to greatest land use and anthropogenic input,were distinct from other sediments in the Gulf of Paria.This was due to higher Pb,Zn,Cu and Hg concentrations (3.53-73.30 µg g-1 ,45.8-313.9 µg g-1 ,8.43-39.71 µg g-1 and 0.03-0.10 µg g-1 ,respectively).Sediments further from the coast were also distinct due to their higher Al,Fe,Cr and Mn concentrations (1.37-3.16 mg g-1 ,9.51-18.91 mg g-1 ,17.22-28.41 µg g-1 and 323.6 -1,564.2 µg g-1 ,respectively).Cd and Pb were higher in the wet season while Ni was higher in the dry season.Pb,Zn,Cu and Hg were correlated with each other and with TOC.Correlation was also observed between Al,Fe,Cr,Mn and Ni.Al,Fe,Cr and Mn were correlated with percentage clay in sediments.The results suggest that Pb,Zn, Cu and Hg are preferentially removed by organic matter,which settles at the river-mouths,while Al,Fe,Cr,Mn, and Ni become associated with clay minerals and are transported away from the coast.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El Golfo de Paria recibe metales pesados de zonas urbanas,industriales y agrícolas,además de aguas negras y aguas servidas,tanto de la costa occidental,como de tierra adentro de Trinidad.Se usaron concentraciones de metales pesados no residuales para determinar la distribución espacial de metales pesados en sedimentos en el Golfo de Paria. Se extrajeron muestras de sedimentos superficiales en 37 estaciones,que incluían la boca de 11 ríos principales que fluyen al golfo.Las estaciones fueron muestreadas dos veces durante la época lluviosa (julio 1998 y noviembre/ diciembre 1998)y dos en la época seca (marzo 1999 y abril 1999).Se analizó en los sedimentos cobre (Cu),cinc (Zn),plomo (Pb),mercurio (Hg),cadmio (Cd),níquel (Ni),cromo (Cr),hierro (Fe),manganeso (Mn),aluminio (Al),Carbón Orgánico Total (COT)y tamaño de grano. El análisis de componentes principales muestra que los sedimentos de las bocas de los ríos con cuencas más deforestadas y con mayor impacto antropogénico,son distintos del resto.Esto se debió a concentraciones mayores de Pb,Zn,Cu y Hg (3.53-73.30 µg g-1 ,45.8-313.9 µg g-1 , 8.43-39.71 µg g-1 y 0.03-0.10 µg g-1, respectivamente). Los sedimentos más alejados de la costa también eran distintos por sus mayores concentraciones de Al,Fe,Cr y Mn (1.37-3.16 mg g-1, 9.51-18.91 mg g-1, 17.22-28.41 µg g-1 y 323.6 -1,564.2 µg g-1 ,respectivamente).Cd y Pb fueron mayores en la época húmeda,mientras que Ni fue mayor en la época seca.Matrices de correlación de Pearson muestran que Pb,Zn,Cu y Hg estaban correlacionados entre si y con el COT.Se observó correlación también entre Al,Fe,Cr,Mn y Ni.Estos metales estaban correlacionados con el porcentaje de arcilla en los sedimentos.Pb,Zn,Cu y Hg son removidos preferiblemente por la materia orgánica que se asienta en la boca de los ríos,mientras que Al,Fe,Cr,Mn y Ni se asocian con las arcillas y son transportados lejos de la costa.</p></abstract>
<kwd-group>
<kwd>Heavy metals</kwd>
<kwd>spatial distribution</kwd>
<kwd>sediments</kwd>
<kwd>Trinidad</kwd>
<kwd>Caribbean</kwd>
<kwd>Metales pesados</kwd>
<kwd>distribución espacial</kwd>
<kwd>sedimentos</kwd>
<kwd>Trinidad</kwd>
<kwd>Caribe</kwd>
</kwd-group>
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<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
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<article-id>S0034-77442005000300009</article-id>
<title-group>
<article-title xml:lang="en">Heavy metals in sediments,mussels and oysters from Trinidad and Venezuela</article-title>
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<aff id="A01">
<institution>,Universidad de Oriente  </institution>
<addr-line> </addr-line>
<country>Venezuela</country>
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<aff id="A02">
<institution>,University of the West Indies  </institution>
<addr-line>St.Augustine </addr-line>
<country>Trinidad</country>
</aff>
<aff id="A03">
<institution>,University of the West Indies  </institution>
<addr-line>St.Augustine </addr-line>
<country>Trinidad</country>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
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<pub-date pub-type="epub">
<year>2005</year>
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<volume>53</volume>
<fpage>41</fpage>
<lpage>51</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300009&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300009&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300009&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The Gulf of Paria is bordered by both Trinidad and Venezuela,from which various metallic pollutants and other contaminants can originate.The Gulf is still a significant source of fish,crabs and shellfish for human consumption to both countries,where concerns over the quality of this marine environment have been long expressed but never properly addressed.In addition,the circulatory current patterns in the Gulf ensure that contaminants originating from either country are likely to affect both countries eventually.Heavy metals were determined in oysters (Crassostrea rhizophorae and C.virginica ),green mussels (Perna viridis )and sediments from the Gulf of Paria.Samples were obtained at four sites in Trinidad and three sites in Venezuela in the Gulf of Paria,in addition to comparative samples collected from three sites on the north coast of Venezuela.Edible tissues of twelve shellfish from each location were blended and aliquots digested with concentrated nitric acid, for extraction of cadmium,chromium,copper,lead,nickel and zinc.The solutions were analysed by flame atomic absorption spectroscopy.Mercury was extracted with a mixture of nitric,hydrochloric and sulphuric acids and determined by cold vapour atomic absorption.Sediments were oven-dried at 60°C, before being similarly extracted.Results showed that mercury in sediments at all sites in Trinidad and Venezuela exceeded NOAA and Canadian sediment quality guidelines,while cadmium, copper, nickel, lead and zinc also exceeded these guidelines at several sites.Heavy metal levels in oysters and green mussels varied widely with location. However,oysters from the Gulf of Paria contained significantly higher mean levels of cadmium,copper,nickel and zinc than those from the north coast of Venezuela, but this difference was not apparent in mussels.Cadmium, mercury and zinc in sediments were significantly correlated with those of mussels,but not of oysters,in which copper and zinc at several sites in the Gulf of Paria exceeded local maximum permissible levels (Cu =20 µg g-1 wet wt; Zn =50 µg g-1 wet wt)for human consumption. These findings indicate that while mussels may be better biological indicators of heavy metal pollution in sediments than oysters,the latter may provide copper and zinc contamination.Further research is needed to determine the most appropriate biological indicators of heavy metal and other pollutants in the local marine environment and to develop protocols for their use.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El Golfo de Paria está rodeado por Trinidad y Venezuela y es una fuente significativa de peces y moluscos para el consumo humano.Se extrajo muestras de ostras (Crassostrea rhizophorae y C.virginica ),mejillones (Perna viridis )y sedimentos de cuatro sitios de Trinidad y tres de Venezuela en el golfo,así como muestras de tres localidades de la costa norte de Venezuela.El tejido comestible homogenizado de 12 moluscos de cada localidad fue usado para la extracción de metales pesados.El cadmio, cromo,cobre,plomo,níquel y zinc fueron analizados por espectroscopía de absorción atómica a la llama y el mercurio fue determinado por vapor al frío.Las ostras del Golfo de Paria presentaron concentraciones significativamente más altas de cadmio,cobre,níquel y zinc que las de la costa norte de Venezuela;pero esa diferencia no fue aparente en los mejillones.El mercurio en los sedimentos en todos los sitios y también el cadmio,cobre,níquel,plomo y zinc de varios sitios excedieron los niveles permisibles de las normas canadienses y estadounidenses.Los valores de cadmio, mercurio y zinc en los sedimentos se correlacionaron significativamente con los de los mejillones,pero no con los de las ostras.En las ostras los valores de cobre y zinc en varios sitios en el Golfo de Paria excedieron los límites máximos permitidos para el consumo humano.Los mejillones pueden ser mejores indicadores de contaminación de metales pesados en sedimentos,pero las ostras pueden indicar mejor la contaminación por cobre y zinc.Se necesita determinar el indicador biológico más apropiado en la determinación de metales pesados y otros contaminantes en el ambiente marino local,y desarrollar protocolos para su uso.</p></abstract>
<kwd-group>
<kwd>Heavy metals</kwd>
<kwd>sediments</kwd>
<kwd>oysters</kwd>
<kwd>mussels</kwd>
<kwd>Gulf of Paria</kwd>
<kwd>Metales pesados</kwd>
<kwd>sedimentos</kwd>
<kwd>ostras</kwd>
<kwd>mejillones</kwd>
<kwd>Golfo de Paria</kwd>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300010&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300010&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300010&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The use of chemical pesticides and herbicides has increased environmental pollution and affected ichthyofauna in the watersheds where they are used.We studied the effect of an herbicide, triazine, on the kidneys of two species (Caquetaia kraussii and Colossoma macropomum )widely found in Caribbean and South American rivers.In Venezuela,these species are abundant and have a high aquaculture potential because they may be cultured and reproduced in captivity.Four kidney samples from juveniles of each species exposed to the herbicide were examined by Transmission Electron Microscopy.Kidney tubule alterations included loss of plasmalemma and cell interdigitations, misshaped mitochondria,decrease in rough endoplasmic reticulum and free polysomes,and the presence of autophagic vacuoles and primary lysosomes.These alterations at the cellular level may explain fish behaviour in terms of kidney tubule pathology,and relative amounts and conditions of organelles within affected cells.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El uso de compuestos químicos como plaguicidas y como herbicidas ha incrementado la contaminación ambiental,afectando la ictiofauna que vive en ríos y depósitos de agua.Estudiamos el efecto de un herbicida (2-cloro-4,6-bis-etlamina-s-triazina)sobre el riñón de dos especies de peces (Caquetaia kraussii y Colossoma macropomum ),ampliamente encontradas en los ríos caribeños y sudamericanos.En Venezuela son abundantes y tienen un alto potencial en acuacultura debido a que pueden ser cultivados y reproducidos en cautiverio.Se disectó el riñón a cuatro individuos jóvenes de cada especie que habían sido expuestos al herbicida y se les examinó con Microscopía Electrónica de Transmisión.Se encontraron alteraciones en los túbulos del riñón que incluían pérdida de plasmalema e interdigitaciones celulares,mitocondrias alteradas, disminución en el retículo endoplásmico,polisomas libres y la presencia de vacuolas autofágicas y lisosomas primarios.Estas alteraciones a nivel celular pueden explicar la conducta de los peces en términos de patología de los túbulos del riñón y las cantidades relativas y condiciones de organelas dentro de las células afectadas.</p></abstract>
<kwd-group>
<kwd>Caquetaia kraussii</kwd>
<kwd>Colossoma macropomum</kwd>
<kwd>kidney</kwd>
<kwd>herbicide</kwd>
<kwd>ultrastructure</kwd>
<kwd>pathology</kwd>
<kwd>stress markers</kwd>
<kwd>Caquetaia kraussii</kwd>
<kwd>Colossoma macropomum</kwd>
<kwd>riñón</kwd>
<kwd>hierbicida</kwd>
<kwd>ultraestructura</kwd>
<kwd>patología</kwd>
<kwd>marcadores de estrés</kwd>
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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0034-77442005000300011</article-id>
<title-group>
<article-title xml:lang="es">The occurrence of black corals in Jamaican reef environments, with special reference to Stichopathes lutkeni (Antipatharia:Antipathidae)</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Warner</surname>
<given-names>G.F</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution>,University of the West Indies  </institution>
<addr-line>Mona Kingston 7</addr-line>
<country>Jamaica</country>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
</pub-date>
<volume>53</volume>
<fpage>61</fpage>
<lpage>66</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300011&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300011&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300011&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The purpose of this study was to record the species of Antipatharia on Jamaican reefs and to carry out limited studies on densities and sizes of the common species.In addition,a cliff face created by dredging in 2002 provided the opportunity to study growth of newly settled colonies.Observations since 1998 and measurements since 2001 were made using SCUBA at depths down to 35 m.Seven species of Antipatharia were observed on steep coral reef escarpments below 25 m depth.The commonest species was the unbranched &quot;wire coral &quot; Stichopathes lutkeni .Other common species included the fan-shaped black corals Antipathes atlantica and A. gracilis .Frequently encountered species included commercially important A.caribbeana and a species with an unusual,scrambling growth form, A. rubusiformis.The other major commercial species in the Caribbean, Plumapathes pennacea ,and a cave-dwelling species,A.umbratica ,were rarely observed.Greatest black coral abundance occurred on steep slopes of hard substrata in low light intensity but exposed to the long-shore current. Combined densities of the commoner Antipatharia at 30 m deep at Rio Bueno on the north coast,ranged from 0.1 to 2.5 m-2 (eleven 10 m x 1 m belt transects,1-25 colonies per transect,68 colonies in total).Forty-six of the 68 colonies were S.lutkeni ,while nearby at Discovery Bay at 30-35 m,55 out of 59 colonies were S.lutkeni. There was a significant difference between the mean length of colonies in these two populations of S.lutkeni (100 cm and 80 cm,respectively),probably relating to habitat.A third population of S.lutkeni growing at 15-20 m deep on the recently dredged cliff had a much smaller mean length of 36.6 cm (n=27).The largest individual measured 83 cm long,indicating a minimum growth rate of the unbranched corallum of 2.1 mm per day.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El propósito de este estudio fue registrar las especies de Antipatharia en los arrecifes de Jamaica y realizar estudios preliminares sobre densidades y tamaños de las especies comunes.Además,una pared vertical creada por dragado en el 2002 permitió determinar el crecimiento de colonias recién asentadas.Hice observaciones desde 1998 y medidas desde el 2001 con equipo de buceo tipo &quot;SCUBA &quot;hasta 35 m de profundidad.Se identificaron siete especies de Antipatharia en paredes empinadas de arrecifes coralinos a más de 25 m de profundidad.La especie más común fue el coral negro no ramificado Stichopathes lutkeni .Otras especies comunes incluyen el coral negro con forma de abanico Antipathes atlantica y Antipathes gracilis .Las especies frecuentes incluyen una comercialmente importante,Antipathes caribbeana y una especie con un crecimiento inusual en forma de trepadora, Antipathes rubusiformis.Se observó poco la otra especie de importancia comercial en el Caribe,Plumapathes pennacea ,y la cavernícola Antipathes umbratica .La mayor abundancia de corales negros se dio en paredes empinadas de sustratos duros con poca iluminación pero expuestos a la corriente a lo largo de la costa.Las densidades combinadas de las especies más comunes de Antipatharia a 30 m de profundidad en Río Bueno en la costa norte,tenían un ámbito entre 0.1 y 2.5 m-2 (once transectos de 10 m x 1 m, 1-25 colonias por transecto,68 colonias en total).Cuarenta y seis de las 68 colonias eran S.lutkeni ,mientras cerca de allí,en Discovery Bay a 30-35 m,55 de las 59 colonias eran S.lutkeni .Había una diferencia significativa entre el tamaño promedio de colonias en estas dos poblaciones de S.lutkeni (100 cm y 80 cm,respectivamente),probablemente relacionada al hábitat.Una tercera población de S. lutkeni creciendo a 15-20 m de profundidad en la pared recién dragada tenía un tamaño promedio mucho más pequeño,36.6 cm (n=27).El individuo más grande midió 83 cm de largo,indicando un crecimiento mínimo del corallum sin ramificar de 2.1 mm por día.</p></abstract>
<kwd-group>
<kwd>Black coral</kwd>
<kwd>Antipatharia</kwd>
<kwd>Jamaica</kwd>
<kwd>Stichopathes</kwd>
<kwd>Antipathes</kwd>
<kwd>Discovery Bay</kwd>
<kwd>Rio Bueno</kwd>
<kwd>Coral negro</kwd>
<kwd>Antipatharia</kwd>
<kwd>Jamaica</kwd>
<kwd>Stichopathes</kwd>
<kwd>Antipathes</kwd>
<kwd>Bahía Discovery Bay</kwd>
<kwd>Rio Bueno</kwd>
</kwd-group>
</article-meta>
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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
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<publisher-name>Universidad de Costa Rica</publisher-name>
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<institution>,Instituto Oceanográfico de Venezuela  </institution>
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<pub-date pub-type="epub">
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<lpage>73</lpage>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300012&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300012&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300012&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Fenology and life cylce of Gracilariopsis tenuifrons (Gracilariaceae)at Sucre,Venezuela.The aim of this work was to determine the frequency of different reproductive phases and to induce the germination of spores from tetrasporic and cystocarpic Gracilariopsis tenuifrons from Chacopata and La Peña,Venezuela, under controlled laboratory conditions (temperature 22 ±1 ºC,12L:12D photoperiod,salinity of 36 ±1 PSU and irradiance of 269 µE m-2 s-1).Tetrasporic individuals dominated numerically over gametophitic individuals. The proportion of vegetative algae was very low.Only cystocarpic algae were collected and the spermatangia were absent.Sporulation,germination and formation of algae suggest that they present a Polysiphonia-type life cycle.Algae with reproductive structures were not obtained in the laboratory,</p></abstract>
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<kwd>fenología</kwd>
<kwd>ciclo de vida</kwd>
<kwd>Venezuela</kwd>
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<institution>,Rosenstiel School of Marine and Atmospheric Science  </institution>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300013&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300013&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300013&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>This study examines scleractinian zooxanthellate coral recruitment patterns in the Florida Keys to determine if differences in density or community composition exist between regions.From July to September 2002,nine patch reefs,three in each of the upper,middle and lower Keys,were surveyed for coral recruits (colonies &amp;lt;5 cm in diameter)using randomly placed quadrats and transects.Coral recruits were enumerated, measured,and identified to genus.Fourteen genera of corals were observed across all sites and ranged from five to 13 per site.Densities ranged from 6.29 ±1.92 (mean ±SE)to 39.08 ±4.53 recruits m -2 ,and there were significant site and regional differences in recruit densities. The density of recruits in the upper Keys was significantly lower than in the middle and lower Keys.In addition,the upper Keys were less diverse and had a different recruit size-frequency distribution.The majority of recruits were non-massive scleractinian species that contribute relatively little to overall reef-building processes,a finding that is similar to previous studies. Fewer recruits of massive species were found in the upper Keys compared to the middle and lower Keys.The recruitment patterns of the reefs in the upper Keys could potentially hinder their ability to recover from stress and disturbances.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Se examina los patrones de reclutamiento de corales escleractinios zooxantelados en los Cayos de la Florida para determinar si existen diferencias en densidad o composición de la comunidad en diferentes regiones.Entre julio y setiembre del 2002,se inventariaron los reclutas (colonias de &amp;lt;5 cm de diámetro)usando cuadrantes y transectos al azar en nueve &quot;parches &quot;arrecifales:tres en los cayos del norte,tres en los del medio y tres en los del sur.Todos fueron numerados,medidos e identificados a nivel de género.Se observaron catorce géneros:entre cinco y 13 por sitio.Las densidades tuvieron un ámbito de 6.29 ±1.92 (promedio ±DS)a 39.08 ±4.53 reclutas m-2, con diferencias estadísticamente significativas entre sitios y entre regiones.La densidad de reclutas en los cayos del norte fue significativamente menor que en los demás.Los cayos del norte tuvieron menor diversidad y diferente distribución de tamaños de reclutas.La mayoría de los reclutas eran de especies de escleractinios no masivas,las cuales contribuyen relativamente poco al proceso de crecimiento del arrecife,algo parecido a lo informado en otros estudios. Se encontraron menos reclutas de especies masivas en los cayos del norte.El patrón de reclutamiento en los arrecifes de los cayos del norte podría inhibir potencialmente la recuperación tras &quot;impactos &quot;y perturbaciones.</p></abstract>
<kwd-group>
<kwd>coral</kwd>
<kwd>recruitment</kwd>
<kwd>Florida Keys</kwd>
<kwd>community composition</kwd>
<kwd>scleractinians</kwd>
<kwd>Coral</kwd>
<kwd>reclutamiento</kwd>
<kwd>Cayos de la Florida</kwd>
<kwd>composición comunitaria</kwd>
<kwd>escleractinios</kwd>
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<institution>,University of the West Indies  </institution>
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<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300014&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300014&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300014&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Coral recruitment was examined on terracotta tiles deployed for four six-month periods between March 2001 and April 2003 on the West Fore Reef at Discovery Bay,Jamaica.During each sampling period, four tiles were deployed on each of two arrays at six depths ranging from 3 m to 33 m.Only three Acropora spat recruited to the tiles over the sampling period.The Acropora spat recruited during only one of the four six-month sampling periods and at only one depth,3m.That represents a density of 8 spat m-2 at 3 m depth for one six-month sampling period.Acropora recruitment represented &amp;lt;1 %of the total spat recruiting to the tiles deployed at 3 m during the four sampling periods.Density of acroporids on the West Fore Reef is low.Only one Acropora colony (an A.palmata )was recorded during Point-Quarter surveys of coral cover and density at depths of 3 m,9 m,14 m and 19 m.Considering the paucity of acroporid colonies and the infrequent settlement of acroporid spat on the West Fore Reef,it is unlikely that the historic abundance of A.palmata and A. cervicornis will return soon.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El reclutamiento de corales fue estudiado utilizando placas de cerámica colocadas en cuatro períodos de seis meses,entre marzo de 2001 y abril de 2003,en el Arrecife Frontal Oeste en Discovery Bay,Jamaica.Durante cada período de muestreo se colocaron dos grupos de cuatro placas a seis profundidades,en un ámbito de 3-33 m.Se encontraron tres reclutas de Acropora durante todo el estudio, únicamente a 3 m de profundidad y durante uno de los cuatro períodos.Esto representa una densidad de 8 reclutas m-2 a 3 m,para un semestre de muestreo.Acropora representó &lt;1%del total de reclutas de las placas colocadas a 3 m durante los cuatro períodos de muestreo.Se encontró una densidad baja de acropóridos en el Arrecife Frontal Oeste. Únicamente se encontró una colonia de Acropora palmata durante los censos de cobertura coralina y densidad realizados a profundidades de 3,9,14 y 19 m.Considerando la escasez de colonias de acropóridos y el asentamiento infrecuente de reclutas en el Arrecife Frontal Oeste,la recuperación de la abundancia histórica de A.palmata y A. cervicornis,es poco probable a corto plazo.</p></abstract>
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<kwd>Setting plates</kwd>
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<kwd>Caribe</kwd>
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<given-names>A</given-names>
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<source>Estandarización de un protocolo para la estimación del estatus poblacional de Acropora palmata</source>
<year>2003</year>
<month></month>
<day></day>
<conf-name>Scient. Meeting Asso.Mar.Lab.Caribbean</conf-name>
<conf-loc>Port of Spain </conf-loc>
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<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance">
<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0034-77442005000300015</article-id>
<title-group>
<article-title xml:lang="en">Potential sources of bacteriological pollution for two bays with marinas in Trinidad</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Bullock</surname>
<given-names>Christine Ann</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Moonesar</surname>
<given-names>Indar</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution>,Institute of Marine Affairs  </institution>
<addr-line> </addr-line>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
</pub-date>
<volume>53</volume>
<fpage>91</fpage>
<lpage>103</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300015&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300015&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300015&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Welcome Bay and Chaguaramas Bay in the northwest peninsula of Trinidad contain large marinas and smaller sections of bathing beaches.Bacteriological surveys were conducted at both bays to assess water quality and to determine potential sources of pollution.These surveys were conducted during the wet season of 1996 and the dry season of 1997.Eleven sample stations were established at Welcome Bay and 12 at Chaguaramas Bay.Freshwater samples were collected from rivers and drains within the survey area.Marine water samples were collected from marinas,bathing beaches and inshore and outer areas at both bays.Five water samples were collected from each sampling station during the wet season of 1996 and six during the dry season of 1997.The membrane filter technique was used to determine faecal coliform and Escherichia coli levels in all samples. There was a seasonal effect on water quality,with significantly higher faecal coliform levels in the wet season, when water quality was not in compliance with international standards.This represents a potential health risk in bathing areas.Water quality was better at the outer area of both bays.Water quality at the inner bay areas was most likely adversely affected by land-based sources of pollution identified in this study.These sources include three drains and two rivers,which discharged into the bays.Yachts were apparently not a source of sewage pollution:there was no significant relationship between yacht number and faecal coliform levels.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Las bahías Welcome y Chaguaramas en la península noroeste de Trinidad tienen grandes marinas y secciones pequeñas de playas para bañistas.Se realizaron sondeos bacteriológicos en ambas bahías para determinar la calidad del agua y para señalar fuentes potenciales de contaminación.Estos sondeos fueron realizados durante la época lluviosa de 1996 y la seca de 1997.Once estaciones de muestreo se establecieron en Bahía Welcome y doce en Bahía Chaguaramas.Muestras de agua dulce fueron recolectadas en ríos y drenajes dentro del área de estudio.Muestras de agua de mar fueron recolectadas en las marinas,playas de bañistas,en las secciones internas y externas de las bahías.En cada estación se recolectaron cinco muestras de agua,durante la época lluviosa de 1996 y seis en la época seca de 1997.Los tipos de bacterias enumeradas fueron coliformes fecales y Escherichia coli . La técnica del filtro de membrana fue utilizada para determinar los niveles de bacterias indicadoras en todas las muestras.Se observó un efecto estacional en la calidad del agua,con niveles de bacterias más altos en la época lluviosa que en la seca en ambas bahías.En las zonas de baño los niveles eran potencialmente peligrosos para la salud pública durante la época lluviosa,cuando la calidad del agua no cumplía con las normas internacionales.Había niveles significativamente más altos de coliformes fecales en bahía Welcome y Bahía Chaguaramas en la época lluviosa que en la seca.La calidad del agua en las zonas externas de ambas bahías fue mejor que en las zonas internas.La calidad del agua en la parte interna de la bahía probablemente estaba afectada negativamente por fuentes terrestres de contaminación identificadas en este estudio.Estas fuentes incluyen tres desagües y dos ríos que descargan en las bahías.Los yates aparentemente no eran una fuente de contaminación en las bahías,ya que no había una relación significativa directa entre el número de yates y los niveles de coliformes fecales en bahía Welcome o en bahía Chaguaramas.</p></abstract>
<kwd-group>
<kwd>Bacteriological water quality</kwd>
<kwd>land-based sources</kwd>
<kwd>seasonal effect</kwd>
<kwd>Trinidad</kwd>
<kwd>Welcome Bay</kwd>
<kwd>Chaguaramas Bay</kwd>
<kwd>Calidad bacteriológica del agua</kwd>
<kwd>fuentes terrígenas</kwd>
<kwd>efecto estacional</kwd>
<kwd>Trinidad</kwd>
<kwd>Bahía Welcome</kwd>
<kwd>Bahía Chaguaramas</kwd>
</kwd-group>
</article-meta>
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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0034-77442005000300016</article-id>
<title-group>
<article-title xml:lang="en">Transplantation of benthic species to mitigate impacts of coastal development in Jamaica</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Gayle</surname>
<given-names>Peter M.H</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
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<name>
<surname>Wilson-Kelly</surname>
<given-names>Peter</given-names>
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<name>
<surname>Green</surname>
<given-names>Sean</given-names>
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<xref ref-type="aff" rid="A02"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution>,University of the West Indies  </institution>
<addr-line>Discovery Bay St.Ann</addr-line>
<country>Jamaica</country>
</aff>
<aff id="A02">
<institution>,National Environmental Protection Agency  </institution>
<addr-line> </addr-line>
<country>Jamaica</country>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
</pub-date>
<volume>53</volume>
<fpage>105</fpage>
<lpage>115</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300016&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300016&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300016&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Maintaining regional competitiveness and economic viability for Port Bustamante -Kingston Harbour, Jamaica,required improved accessibility to &quot;Post Panamax &quot;(too large to pass through the Panama Canal)container vessels.Removal of the northern portion of the shallow coral reef at Rackham ’s Cay,which was partially obstructing the western end of the east ship channel,was proposed.This aesthetically valuable reef was used by local fishermen and comprises part of the declared Palisadoes -Port Royal Protected Area.The proposal to transplant certain of the benthic species was advanced to mitigate loss of viable reef components.Between December 2001 and February 2002,sixty thousand items,consisting of reef building massive and branching corals; gorgonians;urchins (Diadema and Tripneustes spp.)and Thalassia meristems were relocated.During dredging,sedimentation rates from suspended solids in the water column were 0.003 g/cm² /day at the control site and 0.008 g/cm² /day at the dredge site.Coral cover in the relocation area increased from 15%to 20%while bare substrate decreased from 27%to 21%.This paper documents the mitigation required;some factors controlling the ecology of Rackham ’s Cay reef;the methodology of the relocation process;and the level of post-dredging survivorship of relocated corals.Political and economic realities of some proposed developments often over-ride ecological considerations. Transplantation of important marine benthic species although time consuming, technically challenging,and expensive,may be one way for developers and ecologists to achieve sometimes disparate goals.This project cost US$1.7 million.The &quot;items &quot;moved were neither unique nor endemic and remain vulnerable to natural and anthropogenic impacts.This project increased public awareness and interest regarding the ecological and economic importance of reef ecosystems.It is anticipated that future coastal and inland developments will benefit from the lessons taught by these mitigative interventions.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Para mantener la competitividad regional y la viabilidad económica del Puerto de Bustamante -Kingston Harbour,Jamaica,se requería mejorar la entrada de buques de contenedores &quot;Post Panamax &quot;(nombre dado a los buques que son demasiado grandes para pasar por el canal de Panamá).Se propuso remover la parte norte del cayo coralino Rackham que obstruía parcialmente el lado oeste del canal del este.Este arrecife,estéticamente valioso,era usado por pescadores y forma parte del Área Protegida Palisadoes -Port Royal.Se propuso transplantar algunos organismos bentónicos para mitigar las pérdidas de elementos arrecifales.Entre diciembre 2001 y febrero 2002,se reubicó unos 60 000 organismos de corales constructores de arrecifes masivos y ramificados,gorgonaceos, erizos (Diadema y Tripneustes spp.)y meristemos de Thalassia .Durante el dragado las cantidades de sedimentos en suspensión fueron de 0.003 g/cm² /día en el sitio testigo y 0.008 g/cm² /día en el sitio de dragado.La cobertura de coral aumentó en el sitio de reubicación de 15%a 20%mientras que el sustrato desnudo disminuyó de 27%a 21%.En este trabajo se documentan los requerimientos para la mitigación; algunos factores que controlan la ecología del arrecife del Cayo Rackham;la metodología del proceso de reubicación; y el nivel de supervivencia de corales reubicados.Es común que se dé más importancia a consideraciones políticas y económicas de algunas propuestas de desarrollo que a las consideraciones ecológicas.El transplante de especies marinas bentónicas importantes,aunque consume mucho tiempo, es técnicamente desafiante y costoso,es una forma en que los &quot;desarrollistas &quot; y los &quot;ecologistas &quot; pueden alcanzar objetivos dispares.Este proyecto costó EEUU$1.7 millones. Los organismos trasladados no eran únicos ni endémicos y siguen siendo vulnerables a impactos naturales y antropogénicos.Sin embargo,este proyecto aumentó la percepción e interés en la importancia ecológica y económica de los arrecifes coralinos.Se anticipa que futuros proyectos de desarrollo costeros y de tierra adentro se van a beneficiar de las lecciones aprendidas durante esta intento de mitigación.</p></abstract>
<kwd-group>
<kwd>Kingston Harbour</kwd>
<kwd>transplant</kwd>
<kwd>corals</kwd>
<kwd>impacts</kwd>
<kwd>dredging</kwd>
<kwd>Puerto de Kingston</kwd>
<kwd>transplantes</kwd>
<kwd>corales</kwd>
<kwd>impactos</kwd>
<kwd>dragados</kwd>
</kwd-group>
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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0034-77442005000300017</article-id>
<title-group>
<article-title xml:lang="en">Aerial and Tidal Transport of Mosquito Control Pesticides into the Florida Keys National Marine Sanctuary</article-title>
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<contrib-group>
<contrib contrib-type="author">
<name>
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<given-names>R.H</given-names>
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<aff id="A01">
<institution>,Mote Marine Laboratory  </institution>
<addr-line>Sarasota Florida</addr-line>
<country>USA</country>
</aff>
<aff id="A02">
<institution>,Perry Institute of Marine Science  </institution>
<addr-line>Key West Florida</addr-line>
<country>USA</country>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
</pub-date>
<volume>53</volume>
<fpage>117</fpage>
<lpage>125</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300017&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300017&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300017&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>This project was undertaken as the initial monitoring program to determine if mosquito adulticides applied along the Florida Keys cause adverse ecological effects in the Florida Keys National Marine Sanctuary (FKNMS).The study monitored the distribution and persistence of two mosquito adulticides,permethrin and dibrom (naled),during three separate routine applications by the Florida Keys Mosquito Control District.The approach was to determine if toxic concentrations of the pesticides entered the FKNMS by aerial drift or tidal transport.The amount of pesticide entering the FKNMS by way of aerial drift was monitored by collection on glass fiber filter pads,set on floats in a grid pattern on either side of the FKNMS.Permethrin was recovered from filter pads on the leeward side for each of the three applications,ranging from 0.5 to 50.1 µg/m² throughout the study.Tidal current transport was monitored by collection of surface and subsurface water samples at each grid site.Tidal transport of naled and dichlorvos (naled degradation product)was apparent in the adjacent waters of the FKNMS.These compounds were detected in subsurface,offshore water at 0.1 to 0.6 µg/l,14 hr after application.Permethrin was not detected in offshore water samples; however, concentrations ranging from 5.1 to 9.4 µg/l were found in surface water from the canal system adjacent to the application route.Comparison of the observed environmental concentrations with toxicity data (permethrin LC-50,96 hr for Mysidopsis bahia =0.02 µg/l)indicated a potential hazard to marine invertebrates in the canals with possible tidal transport to other areas.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Para determinar si los adulticidas de mosquitos,aplicados en los Cayos de la Florida,causan efectos ecológicos adversos en el Santuario Marino Nacional de los Cayos de la Florida,se monitoreó la distribución y persistencia de dos adulticidas de mosquitos.Estos fueron permetrina y dibrom (naled).Se trabajó durante tres aplicaciones rutinarias hechas por la Unidad de Control de Mosquitos de los Cayos de la Florida.La finalidad era determinar si concentraciones tóxicas de los plaguicidas llegaban al santuario por transporte aéreo o por las corrientes de marea.La cantidad de plaguicida que entra por vía aérea fue monitoreada utilizando filtros de fibra de vidrio,montados en flotadores dispuestos sistemáticamente a ambos lados del FKNMS. La Permetrina fue recuperada en filtros a sotavento del santuario durante tres aplicaciones,con un ámbito entre 0.5 y 50.1 µg/m² durante todo el estudio.El transporte por corrientes de marea fue monitoreado recolectando muestras de agua superficiales y subsuperficiales en puntos definidos.Se notó el transporte por mareas de naled y diclorvos (producto degradado de naled)en aguas adyacentes al santuario.Estos compuestos fueron detectados en muestras subsuperficiales en aguas fuera de la costa con concentraciones de 0.1 a 0.6 µg/l,14 hr después de la aplicación.La Permetrina no fue detectada en muestras de agua fuera de la costa;sin embargo,hubo concentraciones de 5.1 a 9.4 µg/l en aguas superficiales del sistema de canales adyacente a la ruta de aplicación. Comparaciones de las concentraciones observadas con información toxicológica (permetrina LC-50,96 hr para Mysidopsis bahia =0.02 µg/l)indican un peligro potencial para invertebrados marinos en los canales y la posibilidad de transporte por mareas a otras áreas.</p></abstract>
<kwd-group>
<kwd>Organophosphate</kwd>
<kwd>pyrethroid</kwd>
<kwd>naled</kwd>
<kwd>dichlorvos</kwd>
<kwd>permethrin</kwd>
<kwd>mosquito adulticides</kwd>
<kwd>Organofosforados</kwd>
<kwd>piretroides</kwd>
<kwd>naled</kwd>
<kwd>diclorvos</kwd>
<kwd>permetrina</kwd>
<kwd>adulticidas de mosquitos</kwd>
</kwd-group>
</article-meta>
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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
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</journal-meta>
<article-meta>
<article-id>S0034-77442005000300018</article-id>
<title-group>
<article-title xml:lang="en">The importance of the marine ornamental reef fish trade in the wider Caribbean</article-title>
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<contrib-group>
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<given-names>A.W</given-names>
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<aff id="A01">
<institution>,Office of Habitat Conservation  </institution>
<addr-line>Silver Spring MD</addr-line>
<country>USA</country>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
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<volume>53</volume>
<fpage>127</fpage>
<lpage>137</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300018&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300018&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300018&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The marine ornamental fish trade began in the 1930s in Sri Lanka,spread to Hawaii and the Philippines in the 1950s,and expanded to a multi-million dollar industry in the 1970s with fisheries established throughout the tropical Pacific,Indian and Atlantic Oceans.Currently,45 countries supply global markets an estimated 14-30 million fish annually,with an import value of US$28-44 million.The largest suppliers are Indonesia and the Philippines,followed by Brazil,Maldives,Vietnam,Sri Lanka and Hawaii.In the tropical Western Atlantic,16 countries have export fisheries, including the U.S.(Florida and Puerto Rico).The U.S.is the world ’s largest buyer,followed by the European Union and Japan.The global trade consists of over 1400 species of reef fishes,of which only about 25 are captive bred on a commercial scale.Damselfish,anemonefish, and angelfish constitute over 50%of the global volume; butterflyfish, wrasses,blennies,gobies,triggerfish,file-fish,hawkfishes,groupers and basselets account for 31%of the trade,and the remaining 16%is represented by 33 families.The most important fishes from the Caribbean are angelfish (six species), seahorses (two species), royal gramma, jawfish,queen triggerfish,redlip blenny,puddingwife,bluehead wrasse,and blue chromis.The Caribbean currently supplies a small percentage of the global trade in marine ornamental species,but ornamental fisheries in this region represent important emerging industries.It is critical that effective ornamental fishery management plans and regulations are developed and enforced,and fishery-dependent and fishery-independent data are collected and utilized in decision making processes to ensure sustainable ornamental fisheries throughout the region.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El comercio de peces marinos ornamentales se inició en la década de 1930 en Sri Lanka y se extendió a Hawai y Las Filipinas en la década de 1950.Posteriormente se convirtió en una industria multimillonaria cuando,en la década de 1970,se establecieron pesquerías a través del Pacífico tropical y los Océanos Índico y Atlántico.Actualmente,45 países suplen los mercados globales con un estimado de 14-30 millones de peces por año,con un valor de US$28- 44 millones.Los mayores exportadores son Indonesia y Filipinas,seguidos por Brasil,Maldivas,Vietnam,Sri Lanka y Hawai.En el Atlántico Occidental tropical,16 países tienen pesquerías de exportación,incluyendo a los Estados Unidos (Florida y Puerto Rico).Estados Unidos es el mayor comprador,seguido de la Unión Europea y Japón. El comercio mundial consiste de más de 1400 especies de peces de arrecife,de las cuales solamente alrededor de 25 son criadas comercialmente.Los peces damiselas, los peces de anémonas y los ángeles,constituyen más del 50%del volumen mundial;mariposas,lábridos,blénidos, góbidos,chanchos,limas,meritos,meros y cabrillas suman el 31%del mercado y el restante 16%está representado por 33 familias.Los peces más importantes del Caribe son los ángeles (seis especies),caballitos de mar (dos especies), bocones,pez chancho reina,blénido de labios rojos, cabeza azul y cromis azul.En la actualidad,el Caribe suple sólo un pequeño porcentaje del mercado mundial de especies ornamentales marinas,sin embargo,las pesquerías ornamentales en esta región representan importantes industrias emergentes.Es crítico que se desarrollen y refuercen planes y regulaciones de manejo efectivos de pesquerías ornamentales y que se recolecte información pesquero-dependiente y pesquero-independiente,que sirva para ser utilizada en los procesos de toma de decisiones,asegurando la sostenibilidad en las pesquerías ornamentales de la región.</p></abstract>
<kwd-group>
<kwd>Aquarium fishes</kwd>
<kwd>ornamental fisheries</kwd>
<kwd>trade in coral reef species</kwd>
<kwd>(CITES)Appendix II</kwd>
<kwd>international trade</kwd>
<kwd>Peces de acuario</kwd>
<kwd>pesquería de ornamentales</kwd>
<kwd>comercio de especies de arrecifes coralinos</kwd>
<kwd>(CITES) Apéndice II</kwd>
<kwd>comercio internacional</kwd>
</kwd-group>
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<copyright-statement/>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300019&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300019&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300019&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>In recent years the collection of tropical marine organisms for the aquarium trade has become perceived as an activity with an unsustainable history as well as obvious potential for rehabilitation through resource-based fisheries management and consumer-oriented product certification.In the case of Puerto Rico, collection of ornamentals has existed for decades,though unregulated due to a weak fisheries law dating from the 1930 ’s.The new Fisheries Law 278 of 1998 enabled new regulatory approaches for marine ornamentals, which were met with serious challenges rooted in (1)an information gap concerning the fishery regarding participant numbers,collection methods and export volumes,and (2)the absence of consultation of fishers by agency regulators.The information gap led to worst-case assumptions of impact by regulators,and a closure of the fishery, which set the stage for threatening personal confrontations and lawsuits,the latter leading to de facto resource management by judicial order.To redress these issues and move management back into the arena of science and public policy,regulators have initiated a three-phase program: (1)characterize fisher numbers, methods and exports,(2)describe populations and biology of commercial species,and (3)propose appropriate fisheries management approaches.This paper describes only the first phase of this program.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>En años recientes,se ha llegado a percibir la captura de organismos marinos tropicales para el comercio de acuario como una actividad poco sostenible,pero a la vez,con potencial de rehabilitarla por medio del manejo del recurso y la certificación del producto para el consumidor.En el caso de Puerto Rico,la recolección de especies ornamentales ha existido durante décadas y ha sido poco regulada a causa de la débil ley sobre pesquerías existente desde la década de 1930.La Ley 278 de las Industrias Pesqueras de 1998 incluyó nuevas regulaciones para los organismos marinos ornamentales.Las regulaciones buscan resolver:(1)la falta de información en esta pesquería respecto al número de participantes,los métodos de captura y los volúmenes de exportación,y (2)la falta de consulta a pescadores por parte de las agencias reguladoras.La falta de información llevó a los reguladores a suponer que esta actividad tendría el peor impacto,por lo que clausuraron la actividad, produciéndose confrontaciones personales y procesos judiciales. Éstos últimos condujeron a la intervención de la pesquería por orden judicial.Para enderezar estas situaciones y para hacer regresar de nuevo la administración al ámbito de la ciencia y del orden público,los reguladores han iniciado un programa de tres fases:(1)inventariar el número de pescadores,los métodos y las exportaciones,(2)describir las poblaciones y biología de las especies comerciales,y (3)proponer estrategias apropiadas para el manejo de esta industria pesquera.Este artículo describe la primera fase de este programa.</p></abstract>
<kwd-group>
<kwd>Ornamental fisheries</kwd>
<kwd>fisheries management</kwd>
<kwd>Caribbean reef fisheries</kwd>
<kwd>regulatory policy</kwd>
<kwd>sustainable fisheries</kwd>
<kwd>Puerto Rico</kwd>
<kwd>Pesquería de ornamentales</kwd>
<kwd>manejo de pesquerías</kwd>
<kwd>pesquerías del Caribe</kwd>
<kwd>política regulatoria</kwd>
<kwd>pesquería sostenible</kwd>
<kwd>Puerto Rico</kwd>
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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id>S0034-77442005000300020</article-id>
<title-group>
<article-title xml:lang="en">Organization and operation of the marine ornamental fish and invertebrate export fishery in Puerto Rico</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>LeGore</surname>
<given-names>Richard S</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Hardin</surname>
<given-names>Mark P</given-names>
</name>
<xref ref-type="aff" rid="A02"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Ter-Ghazaryan</surname>
<given-names>Diana</given-names>
</name>
<xref ref-type="aff" rid="A03"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution>,LeGore Environmental Associates,Inc.  </institution>
<addr-line> FL</addr-line>
<country>USA</country>
</aff>
<aff id="A02">
<institution>,Greystone Environmental Consultants,Inc.  </institution>
<addr-line> CO</addr-line>
<country>USA</country>
</aff>
<aff id="A03">
<institution>,Florida International University  </institution>
<addr-line> FL</addr-line>
<country>USA</country>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
</pub-date>
<volume>53</volume>
<fpage>145</fpage>
<lpage>153</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300020&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300020&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300020&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>This fishery was examined utilizing public records,stakeholder interviews,and operational site visits to describe the fishery for the Puerto Rico Coral Reef Advisory Committee as a first step toward development of policies for the effective management of these natural resources.The fishery is not large,including fewer than 20 licensed fishers operating primarily on the west end of the island.Only three operators export product,with the remaining fishers providing specimens to the exporters based upon customer orders.Most collection of coral reef species occurs over hard rubble zones mixed with relic reef structures and rock,or on the sides and frontal areas of active reefs.Other species are collected from among mangrove prop root zones,tidal flats,and seagrass beds.Collections are made using simple barrier and dip nets for fish and motile invertebrates such as shrimp. Invertebrates such as crabs,starfish,and sea cucumbers are commonly collected by overturning small rocks, gathering the specimens,and then replacing the rocks in their original positions.Specimens are carried to the boat and transferred to individual cup holders to maximize survival.Although statements concerning former use of chemicals to assist capture were noted,no evidence of current chemical use was observed.Specimens are held in re-circulating seawater systems onshore until collections are aggregated and shipped.The fishery strives to operate with mortality of &lt;1%,as mortalities of &gt;3%are described as unacceptable to customers.More than 100 fish species are collected in this fishery,but the top ten species account for &gt;70%of the total numbers and &gt;60% of the total value of the fishery,with a single species,Gramma loreto (Royal Gramma),comprising &gt;40%of the numbers. More than 100 species of invertebrates are collected,but this fishery is also dominated by a handful of species,including anemones,hermit crabs,turbo snails,serpent starfish,and feather duster polychaetes.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Se estudió la pesquería de peces e invertebrados para acuarios,por comisión del Comité Consultor de Arrecifes Coralinos de Puerto Rico.Se usaron registros públicos, entrevistas con empresarios y pescadores,y visitas a los sitios de operación.La pesquería no es grande:menos de 20 pescadores con licencia que operan principalmente en el extremo occidental de la isla.Únicamente tres exportan el producto,el resto provee especímenes a los exportadores según la demanda.La captura de peces se da principalmente en zonas de escombros coralinos mezclados con restos arrecifales y roca,o en los lados y áreas frontales de arrecifes vivos.Otras especies son recolectadas entre las raíces aéreas de los manglares,zona intermareal y &quot;pastizales &quot; marinos.Se utilizan chinchorros y redes de mano para peces e invertebrados móviles como el camarón.Cangrejos,estrellas y pepinos de mar,así como otros invertebrados,son recogidos comúnmente volcando rocas pequeñas,sacando los individuos y después colocando las rocas en su lugar original.Los especímenes son llevados al bote y se transfieren a envases individuales para aumentar la supervivencia.Aunque existen informes previos de captura con sustancias químicas,no se observó ninguna evidencia en esta ocasión.Los especímenes se dejan en sistemas de recirculación de agua en la costa hasta el día del embarque.La pesquería se esfuerza en mantener índices de mortalidad &lt;1%,ya que una mortalidad mayor al 3%es inaceptable para los clientes.Aunque se recolecta más de 100 especies de peces,tan solo diez de ellas representan más del 70%de los individuos y más del 60% del valor de esta pesquería.Gramma loreto representa más del 40%de la cantidad total.Asimismo,se recolecta más de 100 especies de invertebrados (especialmente anémonas,cangrejos ermitaños,ofiúridos,&quot;caracoles turbo &quot; y poliquetos tubícolas.</p></abstract>
<kwd-group>
<kwd>ornamentals</kwd>
<kwd>marine ornamentals</kwd>
<kwd>coral reef fisheries</kwd>
<kwd>reef management</kwd>
<kwd>Caribbean fisheries</kwd>
<kwd>sustainable fisheries management</kwd>
<kwd>Ornamentales marinos</kwd>
<kwd>pesquería de peces de arrecife</kwd>
<kwd>manejo de pesquerías</kwd>
<kwd>pesquerías del Caribe</kwd>
<kwd>manejo de pesca sostenible</kwd>
</kwd-group>
</article-meta>
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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420050003</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
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<article-meta>
<article-id>S0034-77442005000300021</article-id>
<title-group>
<article-title xml:lang="en">Linking larval history to juvenile demography in the bicolor damselfish Stegastes partitus (Perciformes:Pomacentridae)</article-title>
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<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Nemeth</surname>
<given-names>Richard S</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
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<aff id="A01">
<institution>,University of New Hampshire  </institution>
<addr-line> </addr-line>
<country>US</country>
</aff>
<pub-date pub-type="pub">
<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
</pub-date>
<volume>53</volume>
<fpage>155</fpage>
<lpage>163</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300021&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300021&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300021&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Otolith-based reconstructions of daily larval growth increments were used to examine the effect of variation in larval growth on size and age at settlement and post-settlement growth,survival and habitat preferences of juvenile bicolor damselfish (Stegastes partitus Poey).During August 1992 and 1994,newly settled S. partitus were collected from Montastraea coral heads and Porites rubble piles in Tague Bay,St.Croix,U.S. Virgin Islands (17 °45 ’ N,64 °42 ’ W).Daily lapillar otolith increments from each fish were counted and measured with Optimas image analysis software.S.partitus pelagic larval duration was 23.7 d in 1992 (n =70)and 24.6 d in 1994 (n =38)and larval age at settlement averaged 13.0 mm total length both years.Analysis of daily otolith increments demonstrated that variation in larval growth rates and size and age at settlement had no detectable effect on post-settlement survivorship but that larger larvae showed a preference for Montastraea coral at settlement.Late larval and early juvenile growth rates showed a significant positive relationship indicating that growth patterns established during the planktonic stage can span metamorphosis and continue into the benthic juvenile phase.Larval growth rates during the first two weeks post-hatching also had a strong effect on age to developmental competence (ability to undergo metamorphosis)in both 1992 and 1994 with the fastest growing larvae being 8 d younger and 0.8 mm smaller at settlement than the slowest growing larvae.These differential growth rates in early stage larvae established trajectories toward larval developmental competence and may prove important in biogeographical studies of larval dispersal.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Reconstruyendo aumentos diarios de otolitos se compará la variación en crecimiento larval sobre el tamaño y la edad de asentamiento,y el crecimiento post-acentamiento, sobrevivencia y preferencia de hábitat,del pez damisela bicolor (Stegastes partitus Poey)joven.En agosto de 1992 y 1994 se recolectó S.partitus recientemente asentados en colonias de Montastraea y en escombros de Porites en Tague Bay,St.Croix,Islas Vírgenes Estadounidenses (17 °45 ’ N,64 °42 ’ W).A cada pez se le midió el aumento diario en el otolito con el programa de análisis de imágenes Optimas .El estadío de larva pelágica de S.partitus duró 23.7 d en 1992 (n =70)y 24.6 d en 1994 (n =38)y,al asentarse,el largo total promedio en ambos años fue de 13.0 mm.Los otolitos indican que las variaciones en las tasas de crecimiento,tamaño y edad de asentamiento no tienen un efecto detectable en la sobrevivencia post-asentamiento.Sin embargo,las larvas más grandes mostraron preferencia por asentarse en el coral Montastraea .Las tasas de crecimiento larval tardío y juvenil temprano tuvieron una correlación positiva significativa:los patrones de crecimiento establecidos durante el estadío planctónico pasan la metamorfosis y continúan en la fase juvenil béntica.La tasa de crecimiento larval durante las primeras dos semanas después de eclosionar también tiene un efecto sobre la edad a la que concluyeron su desarrollo (momento de la metamorfosis)en 1992 y 1994.Las larvas de crecimiento rápido fueron 8 d más jóvenes y 0.8 mm más pequeñas al asentarse.Este crecimiento diferencial en el estadío larval temprano establece diferencias en la duración del desarrollo larval y puede ser importante en estudios biogeográficos sobre dispersión de larvas.</p></abstract>
<kwd-group>
<kwd>Larval to juvenile transition</kwd>
<kwd>otoliths</kwd>
<kwd>metamorphosis</kwd>
<kwd>Caribbean</kwd>
<kwd>Stegastes partitus</kwd>
<kwd>Transición de larva a adulto</kwd>
<kwd>otolitos</kwd>
<kwd>metamorphosis</kwd>
<kwd>Caribe</kwd>
<kwd>Stegastes partitus</kwd>
</kwd-group>
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<year>2005</year>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300022&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300022&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300022&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The spatial distribution of seagrass and algae communities can be difficult to determine in large,shallow lagoon systems where high turbidity prevents the use of optical methods like aerial photography or satellite imagery.Further complications can arise when algae are not permanently attached to the substratum and drift with tides and currents.A study using acoustic seafloor discrimination was conducted in the Indian River Lagoon (Florida,USA)to determine the extent of drift algae and seagrass.Acoustic surveys using the QTC View V system based on 50 and 200 kHz transducers were conducted near Sebastian Inlet.Results indicate that areas of seagrass can be identified,and are mixed with a high abundance of drift algae.Nearest-neighbor extrapolation was used to fill in spaces between survey lines and thus obtain spatially cohesive maps.These maps were then ground-truthed using data from towed video and compared using confusion matrices.The maps showed a high level of agreement (60%)with the actual distribution of algae,however some confusion existed between bare sand and algae as well as seagrass.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>La distribución espacial de comunidades de pastos marinos y algas puede ser difícil de determinar en sistema lagunares grandes y someros donde la alta turbidez no permite el uso de métodos ópticos,como fotografías aéreas e imágenes satelitales. Complicaciones adicionales pueden surgir cuando las algas no están adheridas permanentemente al sustrato y derivan con las mareas y corrientes.Se realizó un estudio utilizando discriminación acústica del fondo marino en el Indian River Lagoon (Florida,EUA) para determinar la cantidad de algas y pastos que derivan. Se realizaron sondeos acústicos en el Sebastian Inlet con el sistema QTC View V y transductores de 50 y 200 kHz.Las áreas de pastos marinos pudieron ser identificadas,y están mezcladas con una gran cantidad de algas a la deriva.Se rellenó los espacios sin datos con extrapolaciones basadas en la técnica del &quot;vecino más cercano &quot;,produciendo un mapa espacialmente coherente.Comprobaciones de campo con video y &quot;matrices de confusión &quot;indican que los mapas tienen un alto nivel de concordancia (60%)con la distribución real de las algas;sin embargo,hubo cierta confusión entre arena y algas,y entre arena y pastos marinos.</p></abstract>
<kwd-group>
<kwd>Acoustic ground discrimination</kwd>
<kwd>remote sensing</kwd>
<kwd>seagrass</kwd>
<kwd>drift algae</kwd>
<kwd>Indian River Lagoon</kwd>
<kwd>Florida</kwd>
<kwd>Discriminación acústica del fondo</kwd>
<kwd>sensores remotos</kwd>
<kwd>pastos marinos</kwd>
<kwd>algas a la deriva</kwd>
<kwd>Laguna Río Indio</kwd>
<kwd>Florida</kwd>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300023&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300023&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300023&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The Atlantic coast of Broward County,Florida (USA)is paralleled by a series of progressively deeper, shore-parallel coral reef communities.Two of these reef systems are drowned early Holocene coral reefs of 5 ky and 7 ky uncorrected radiocarbon age.Despite the ease of access to these reefs,and their major contribution to the local economy,accurate benthic habitat maps of the area are not available.Ecological studies have shown that different benthic communities (i.e.communities composed of different biological taxa)exist along several spatial gradients on all reefs.Since these studies are limited by time and spatial extent,acoustic surveys with the QTCView V bottom classification system based on a 50 kHz transducer were used as an alternative method of producing habitat maps.From the acoustic data of a 3.1 km² survey area,spatial prediction maps were created for the area.These were compared with habitat maps interpreted from in situ data and Laser Airborne Depth Sounder (LADS)bathymetry,in order to ground-truth the remotely sensed data.An error matrix was used to quantitatively determine the accuracy of the acoustically derived spatial prediction model against the maps derived from the in situ and LADS data sets.Confusion analysis of 100 random points showed that the system was able to distinguish areas of reef from areas of rubble and sand with an overall accuracy of 61%.When asked to detect more subtle spatial differences,for example,those between distinct reef communities,the classification was only about 40%accurate.We discuss to what degree a synthesis of acoustic and in situ techniques can provide accurate habitat maps in coral reef environments,and conclude that acoustic methods were able to reflect the spatial extent and composition of at least three different biological communities.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>La costa Atlántica del Condado de Broward,Florida (EEUU)es paralela a una serie de arrecifes coralinos lineales de creciente profundos.Dos de estos sistemas arrecifales del Holoceno Temprano (cinco mil y siete mil años) son arrecifes coralinos sumergidos.Aunque estos arrecifes son de fácil acceso y contribuyen en forma significativa a la economía local,no existen mapas detallados de los hábitats bentónicos.Los estudios ecológicos han demostrado que diferentes comunidades bentónicas (i.e.comunidades compuestas por diferentes táxones)existen a lo largo de gradientes espaciales de todos los arrecifes.Como estos estudios tienen limitaciones temporales y espaciales,hicimos sondeos acústicos con el sistema de clasificación béntica QTCView V basado en transductores de 50 kHz, como un método alternativo para producir mapas de hábitat.De la información acústica de una área de 3.1 km² ,se generaron mapas predictivos para el área.Posteriormente se compararon con mapas de hábitat hechos in situ y con batimetría generada con una Sonda de Batimetría Láser Aérea (Laser Airborne Depth Sounder:LADS),para comprobar la precisión de los datos del sensor remoto.Se usó una matriz de errores para determinar la fidelidad del modelo espacial predictivo, generado acústicamente,en comparación con los mapas derivados in situ y las bases de datos LADS. Un Análisis de Confusión (errores de predicción)de 100 puntos al azar mostró que el sistema podía diferenciar arrecifes de áreas cubiertas con escombros y arena,con una precisión del 61%.Al tratar de ver diferencias espaciales más sutiles,por ejemplo,entre diferentes comunidades arrecifales,la precisión bajó al 40%.Discutimos hasta que punto una síntesis de técnicas acústicas e in situ pueden proveer mapas de hábitat precisos en ambientes de arrecifes coralinos,y concluimos que los métodos acústicos pueden predecir la extensión espacial y la composición de al menos tres comunidades biológicas.</p></abstract>
<kwd-group>
<kwd>Acoustic seabed classification</kwd>
<kwd>Coral reef community</kwd>
<kwd>Spatial prediction</kwd>
<kwd>Broward County Florida</kwd>
<kwd>Accuracy assessment</kwd>
<kwd>Clasificación acústica de fondos</kwd>
<kwd>arrecifes coralinos</kwd>
<kwd>predicciones espaciales</kwd>
<kwd>Condado Broward</kwd>
<kwd>Florida</kwd>
<kwd>análisis de fidelidad</kwd>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300024&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300024&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300024&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Continuous summit-to-sea maps showing both land features and shallow-water coral reefs have been completed in Puerto Rico and the U.S.Virgin Islands,using circa 2000 Landsat 7 Enhanced Thematic Mapper (ETM+)Imagery.Continuous land/sea terrain was mapped by merging Digital Elevation Models (DEM)with satellite-derived bathymetry.Benthic habitat characterizations were created by unsupervised classifications of Landsat imagery clustered using field data,and produced maps with an estimated overall accuracy of &gt;75%(Tau coefficient &gt;0.65).These were merged with Geocover-LC (land use/land cover)data to create continuous land/ sea cover maps.Image pairs from different dates were analyzed using Principle Components Analysis (PCA)in order to detect areas of change in the marine environment over two different time intervals:2000 to 2001,and 1991 to 2003.This activity demonstrates the capabilities of Landsat imagery to produce continuous summit-to-sea maps,as well as detect certain changes in the shallow-water marine environment,providing a valuable tool for efficient coastal zone monitoring and effective management and conservation.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Se elaboraron mapas de Puerto Rico y las Islas Vírgenes Estadounidenses que muestran la cobertura del suelo y el fondo en arrecifes de coral (&quot;mapas cima-mar) con imágenes del año 2000 del Enhanced Thematic Mapper (ETM+)del satélite Landsat 7.Se fusionaron Modelos de Elevación Digital con batimetría satelital.Se caracterizaron hábitats bentónicos con clasificaciones &quot;no supervisadas &quot; de imágenes de Landsat,agrupando mediante datos de campo,y produciendo mapas con una precisión superior al 75%(coeficiente Tau &gt;0.65).Estas caracterizaciones se combinaron con datos de Geocover-LC (uso /cobertura del suelo)para hacer los mapas.Comparando pares de imágenes mediante Análisis de Componentes Principales se logró identificar las zonas de cambios en los ambientes marinos en dos períodos:2000 a 2001 y 1991 a 2003.Se demostró la capacidad de las imágenes del satélite Landsat para producir mapas continuos cima-mar y para detectar cambios en los ambientes marinos someros,proveyendo así una valiosa herramienta para el monitoreo,el manejo y conservación efectiva de la zona costera.</p></abstract>
<kwd-group>
<kwd>remote sensing</kwd>
<kwd>benthic habitats</kwd>
<kwd>change analysis</kwd>
<kwd>Landsat</kwd>
<kwd>coral reefs</kwd>
<kwd>mapping</kwd>
<kwd>Sensores remotos</kwd>
<kwd>hábitat béntico</kwd>
<kwd>análisis de cambios</kwd>
<kwd>Landsat</kwd>
<kwd>arrecifes coralinos</kwd>
<kwd>mapeo</kwd>
</kwd-group>
</article-meta>
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<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
<issn>0034-7744</issn>
<publisher>
<publisher-name>Universidad de Costa Rica</publisher-name>
</publisher>
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<article-id>S0034-77442005000300025</article-id>
<title-group>
<article-title xml:lang="en">A Geographic Information System (GIS)analysis for trace metal assessment of sediments in the Gulf of Paria,Trinidad</article-title>
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<contrib-group>
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</contrib-group>
<aff id="A01">
<institution>,Information Technology Department  </institution>
<addr-line> </addr-line>
<country>Republic of Trinidad and Tobago</country>
</aff>
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<month>05</month>
<year>2005</year>
</pub-date>
<pub-date pub-type="epub">
<year>2005</year>
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<volume>53</volume>
<fpage>195</fpage>
<lpage>206</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300025&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300025&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300025&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The Gulf of Paria is a semi-enclosed shallow basin with increasing coastal development activities along Trinidad ’s west coast.Sediments present a host for trace metal pollutants from overlying waters,therefore determination of their content is critical in evaluating and detecting sources of marine pollution.This paper presents a Geographic Information System (GIS)analysis of geochemical assessment for trace metals in coastal sediments of the Gulf of Paria.This GIS approach facilitates interpretation of the spatial relationships among key environmental processes.The GIS development involves the integration of spatial and attribute data pertaining to bathymetry,current systems,topography,rivers,land use/land cover and coastal sediments.It employs spatial interpolation and retrieval operations to analyze the total trace metal concentrations of aluminum,copper and lead in the sediments and the clay-enriched sediments,to determine whether they are related to sediment type or are affected by the discharge from anthropogenic sources.Spatial distribution modeling of element concentrations are produced to indicate contamination plumes from possible anthropogenic sources such as rivers entering the Gulf of Paria,and to reveal potential hot spots and dispersion patterns.A direct spatial correlation between clay-enriched sediments and high concentrations of aluminum and lead is detected,however regions of high concentrations of copper and lead indicate a relationship to anthropogenic sources.The effectiveness of GIS for visualization, spatial query and overlay of geochemical analysis is demonstrated.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El Golfo de Paria es una cuenca semi-cerrada de creciente desarrollo en la costa occidental de Trinidad.Los sedimentos presentan una serie de metales contaminantes por lo que es importante la determinación de concentraciones y la detección de sus fuentes.Se presenta un análisis de metales traza en sus sedimentos costeros por Sistema de Información Geográfica (SIG).El SIG facilita la interpretación de las relaciones espaciales de procesos ambientales claves.El SIG integra información espacial sobre batimetría,sistemas de corrientes,topografía,ríos,uso y cobertura del suelo,y los sedimentos costeros.Emplea interpolaciones espaciales y operaciones de búsqueda para analizar las concentraciones de aluminio,cobre y plomo en sedimentos y en los sedimentos ricos en arcillas,para determinar si están relacionados con el tipo de sedimento o afectados por las fuentes humanas de contaminación.Se producen modelos de la distribución espacial de los elementos para indicar &quot;plumas &quot; de sedimentos de posibles fuentes humanas tales como ríos que entran al Golfo de Paria,y para dilucidar potenciales &quot;puntos álgidos &quot; de contaminación y los patrones de dispersión.Se encontró una correlación espacial directa entre sedimentos ricos en arcillas y altas concentraciones de aluminio y plomo,mientras que las regiones con altas concentraciones de cobre y plomo indican una relación con fuentes antropogénicas.Se demostró la utilidad del SIG para visualizar, hacer consultas espaciales y sobreponer los resultados de análisis geoquímicos.</p></abstract>
<kwd-group>
<kwd>Geographic Information System</kwd>
<kwd>spatial interpolation</kwd>
<kwd>geochemical analysis</kwd>
<kwd>trace metal pollution</kwd>
<kwd>Gulf of Paria</kwd>
<kwd>Sistema de Información Geográfica</kwd>
<kwd>interpolación espacial</kwd>
<kwd>análisis geoquímico</kwd>
<kwd>metales traza</kwd>
<kwd>contaminación Golfo de Paria</kwd>
</kwd-group>
</article-meta>
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<article-id>S0034-77442005000300026</article-id>
<title-group>
<article-title xml:lang="en">Biomass,litterfall and decomposition rates for the fringed Rhizophora mangle forest lining the Bon Accord Lagoon,Tobago</article-title>
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<aff id="A01">
<institution>,Institute of Marine Affairs  </institution>
<addr-line> Chaguaramas</addr-line>
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<copyright-statement/>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300026&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300026&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300026&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The mangrove forest that fringes the Bon Accord Lagoon measures 0.8 km² and is dominated by red mangrove (Rhizophora mangle ).This forest forms the landward boundary of the Buccoo Reef Marine Park in Southwest Tobago,and is part of a mangrove-seagrass-coral reef continuum.Biomass and productivity,as indicated by litterfall rates,were measured in seven 0.01 ha monospecific plots from February 1998 to February 1999,and decomposition rates were determined. Red mangrove above-ground biomass ranged between 2.0 and 25.9 kg (dry wt.)m-2 .Mean biomass was 14.1 ±8.1 kg (dry wt.)m-2 yielding a standing crop of 11 318 ±6 488 t. Litterfall rate varied spatially and seasonally.It peaked from May to August (4.2-4.3 g dry wt.m-2 d-1 )and was lowest from October to December (2.3-2.8 g dry wt.m-2 d-1 ).Mean annual litterfall rate was 3.4 ±0.9 g dry wt.m-2 d-1 .Leaf degradation rates ranged from 0.3%loss d-1 in the upper intertidal zone to 1%loss d-1 at a lower intertidal site flooded by sewage effluent.Mean degradation rate was 0.4 ±1%loss d-1 .The swamp produces 2.8 t dry wt.of litterfall and 12 kg dry wt.of decomposed leaf material daily.Biomass and litterfall rates in Bon Accord Lagoon were compared to five similar sites that also participate in the Caribbean Coastal Marine Productivity Programme (CARICOMP).The Bon Accord Lagoon mangrove swamp is a highly productive fringed-forest that contributes to the overall productivity of the mangrove-seagrass-reef complex.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El manglar que bordea la laguna de Bon Accord mide 0.8 km² y predomina el mangle rojo (Rhizophora mangle ).Este manglar es el límite terrestre del Parque Nacional Buccoo Reef en el suroeste de Tobago,y es parte de un continuo de mangles-pastos-arrecifes.En este trabajo se midió la biomasa y productividad,mediante la caída de hojas,y las tasas de descomposición en siete parcelas monoespecíficas de 0.01 ha,de febrero 1998 a febrero 1999.La biomasa sobre el suelo del mangle rojo se registró entre 2.0 y 25.9 kg (peso seco)m-2 .La biomasa promedio fue de 14.1 ±8.1 kg (peso seco)m-2 resultando en un recurso existente de 11 318 ±6488 t.La tasa de caída de hojas varió espacial y temporalmente.El máximo fue entre mayo y agosto (4.2-4.3 g peso seco m-2 d-1 )y el mínimo entre octubre y diciembre (2.3-2.8 g peso seco m-2 d-1 ).La tasa promedio de caída de hojas fue de 3.4 ±0.9 g peso seco m-2 d-1 .La tasa de degradación tuvo un ámbito de 0.3% pérdida d-1 ,en la parte superior de la zona intermareal a 1%pérdida d-1 en la parte inferior de sitios intermareales expuestos a aguas negras.La tasa de degradación promedio fue de 0.4 ±1%pérdida d-1 .Este manglar produjo 2.8 t peso seco de hojas y 12 kg peso seco de hojas descompuestas. La biomasa y las tasas de caída de hojas en Bon Accord fueron comparadas con otros cinco sitios que participan en el Programa del Caribe de Productividad Marino Costera (CARICOMP).El de la laguna de Bon Accord es un manglar marginal altamente productivo que contribuye a la productividad total del complejo mangles-pastos-arrecifes.</p></abstract>
<kwd-group>
<kwd>Rhizophora mangle</kwd>
<kwd>biomass</kwd>
<kwd>litterfall rates</kwd>
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<journal-title>Revista de Biología Tropical</journal-title>
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<surname>Juman</surname>
<given-names>Rahanna A</given-names>
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<institution>,Institute of Marine Affairs  </institution>
<addr-line> Chaguaramas</addr-line>
<country>Trinidad and Tobago</country>
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<month>05</month>
<year>2005</year>
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<pub-date pub-type="epub">
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<volume>53</volume>
<fpage>219</fpage>
<lpage>227</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300027&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300027&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300027&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The Thalassia testudinum dominated seagrass community in the Buccoo Reef/Bon Accord Lagoon Marine Park,measures 0.5 km² and is part of a contiguous coral reef,seagrass bed and mangrove swamp system in southwest Tobago.T.testudinum coverage,productivity and percent turnover rates were measured from February 1998 to February 1999 at four sample locations,while total T.testudinum biomass was measured at two locations in the lagoon from 1992-2002.Productivity and turnover rates varied spatially and seasonally. They were higher in the back-reef area than in the mangrove-fringed lagoon,and were lowest at locations near to a sewage outfall.T.testudinum coverage ranged from 6.6%in the lagoon to 68.5%in the back-reef area while productivity ranged from 3.9 to 4.9 g dry wt m-2 d-1 .Productivity and percentage turnover rates were higher in the dry season (January -June)than in the wet season (July -December).Productivity ranged from 3.0 in the wet season to 5.0 g dry wt m-2 d-1 in the dry season while percentage turnover rates ranged from 4.2%to 5.6%.Total Thalassia biomass and productivity in Bon Accord Lagoon were compared to six similar sites in the Caribbean that also participate in the Caribbean Coastal Marine Productivity Program (CARICOMP).This seagrass community is being negatively impacted by nutrient-enriched conditions.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>La comunidad de pastos marinos de Buccoo Reef/ Parque Nacional Bon Accord Lagoon,dominado por Thalassia testudinum,mide 0.5 km² y es parte de un complejo de arrecifes,lechos de pastos marinos y manglares en el suroeste de Tobago.La cobertura,productividad y tasa de recambio de T.testudinum fueron medidas de febrero 1998 a febrero 1999 en cuatro localidades,mientras que la biomasa total de T.testudinum fue medida en dos localidades en la laguna,entre 1992-2002.La productividad y la tasa de recambio variaron espacialmente y estacionalmente.Fueron mayores en la parte trasera del arrecife que en el manglar y la laguna del arrecife marginal,y fueron menores en localidades cerca de un emisario de aguas negras.La cobertura de T.testudinum tuvo un ámbito de 6.6%en la laguna a 68.5%en la parte trasera del arrecife, mientras que la productividad tuvo un ámbito de 3.9 a 4.9 g peso seco m-2 d-1.La productividad y las tasas de recambio fueron mayores en la época seca (enero a junio)que en la época lluviosa (julio-diciembre).La productividad tuvo un ámbito entre 3.0 en la época húmeda y 5.0 g peso seco m-2 d-1 en la época seca,mientras que las tasas de recambio variaron entre 4.2 y 5.6%.La biomasa total de Thalassia y la productividad en Bon Accord Lagoon fueron comparadas con seis sitios similares en el Caribe que también participan en el Programa de Productividad Marino-Costera del Caribe (CARICOMP).La comunidad de pastos de Bon Accord Lagoon está siendo afectada negativamente por enriquecimiento de nutrimentos.</p></abstract>
<kwd-group>
<kwd>Thalassia testudinum</kwd>
<kwd>Bon Accord Lagoon</kwd>
<kwd>CARICOMP</kwd>
<kwd>productivity</kwd>
<kwd>biomass</kwd>
<kwd>Thalassia testudinum</kwd>
<kwd>Laguna Bon Accord</kwd>
<kwd>CARICOMP</kwd>
<kwd>productividad</kwd>
<kwd>biomasa</kwd>
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<institution>,Buccoo Reef Trust  </institution>
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<copyright-statement/>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300028&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300028&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300028&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Environmental education is a relatively new area on the primary school curriculum of Trinidad and Tobago.Because of the close relationship between human activities and the degradation of the natural environment in Tobago,environmental education will become increasingly important to the preservation and conservation of the island ’s fragile natural resources.Current teaching methods rely heavily on text books and utilise a lecture style that does not promote student interaction. Unfortunately, these methods are not very conducive to environmental education.As such,this paper examines a pilot program in which staff from the Buccoo Reef Trust taught students from 15 primary schools about coral reefs using interactive tools and hands-on methods as described in People &amp;Corals:an Education Package for Primary Schools (People &amp;Corals ).The pilot program ran over an eight week period with prepared lessons being taught every two weeks and student evaluations taking place once before the first lesson and once after the last lesson.The lessons were supplemented with a field trip to a coral reef ecosystem.Despite several challenges that were faced in the implementation process,the overall outcome of the pilot program was successful.Teachers and students reacted positively to the information that was being shared,thereby reinforcing the effectiveness of using a dynamic,active method of teaching to advance environmental education.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>La educación ambiental es un área relativamente nueva en los currículos de las escuelas primarias de Trinidad y Tobago.Debido a la relación entre las actividades humanas y la degradación del ambiente natural,la educación ambiental va a ser cada vez más importante para la preservación y conservación de los frágiles recursos naturales de la Isla de Tobago.Los métodos de enseñanza actuales se basan principalmente en libros de texto y utilizan un estilo de lectura que no promueve la interacción de los estudiantes.Desafortunadamente,éstos métodos no son ideales para la educación ambiental.Así,este artículo examina un programa piloto en el que trabajadores del &quot;Buccoo Reef Trust &quot;enseñaron a estudiantes de 15 escuelas primarias acerca de los arrecifes coralinos usando herramientas interactivas y métodos manuales.Este programa piloto tuvo una duración de ocho semanas,con lecciones cada dos semanas y dos evaluaciones para los estudiantes: antes de la primera lección y después de la última.Las lecciones se complementaron con una gira de campo a un ecosistema de coral.A pesar de algunas dificultades en el proceso de implementación,en general el programa fue un éxito.Los profesores y estudiantes reaccionaron positivamente a la información compartida,reforzando así la necesidad de usar métodos dinámicos y activos para mejorar la enseñanza en educación ambiental.</p></abstract>
<kwd-group>
<kwd>environmental</kwd>
<kwd>education</kwd>
<kwd>Tobago</kwd>
<kwd>coral</kwd>
<kwd>primary school</kwd>
<kwd>Ambiente</kwd>
<kwd>educación</kwd>
<kwd>Tobago</kwd>
<kwd>corales</kwd>
<kwd>escuelas primarias</kwd>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442005000300029&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_abstract&amp;pid=S0034-77442005000300029&amp;lng=en&amp;nrm=iso&amp;tlng=en"></self-uri><self-uri xlink:href="http://www.scielo.sa.cr/scielo.php?script=sci_pdf&amp;pid=S0034-77442005000300029&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Grande Riviere Beach in Trinidad and Tobago is an important nesting site in the Caribbean for the Critically Endangered leatherback sea turtle,Dermochelys coriacea .Community members were concerned that beach erosion and seasonal river flooding were destroying many of the nests deposited annually and thought that a hatchery was a possible solution.Over the 2001 turtle nesting season,the Institute of Marine Affairs (IMA) assessed the spatial and temporal distribution of nests using the Global Positioning System recorded to reference points,and beach dynamics using permanent bench mark profile stations,to determine areas of high risk and more stable areas for nesting.A total of 1449 leatherback nests were positioned.It was evident that at the start of the season in March,the majority of leatherback nests were deposited at the eastern section of the beach. After May,there was a continuing westward shift in nest distribution as the season progressed until August and beach erosion in the eastern section became predominant.The backshore remained relatively stable along the entire beach throughout the nesting season,and erosion was predominant in the foreshore at the eastern section of the beach,from the middle to the end of the season.Similar trends in accretion and erosion were observed in 2000.River flooding did not occur during the study period or in the previous year.With both high risk and more stable regions for turtle nesting available at Grande Riviere Beach,there was no compelling evidence to justify the need for a hatchery.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>La playa de Grande Riviere en Trinidad y Tobago es un sitio importante de anidación en el Caribe de la tortuga baula,Dermochelys coriacea ;una tortuga marina en peligro de extinción.Los residentes estaban preocupados de que la erosión de la playa y las inundaciones estacionales estaban destruyendo muchos de los nidos y pensaron que un criadero era una solución.Durante la temporada de anidación del 2001,el Instituto de Asuntos Marinos de Trinidad y Tobago (Institute of Marine Affairs:IMA) determinó la distribución espacial y temporal de los nidos referenciados con respecto a varios puntos fijados por satélite (Global Positioning System),y la dinámica de la playa usando marcas permanentes del perfil de la playa, para determinar áreas de alto riesgo y áreas estables para los nidos.Se ubicó 1449 nidos.Fue evidente que al inicio de la temporada (marzo),la mayoría de los nidos estaban ubicados en el sector oriental de la playa.De abril a agosto la anidación se fue desplazando hacia el oeste conforme avanzaba la temporada,mientras que la erosión de la playa aumentaba en el sector oriental.La parte trasera se mantiene estable a lo largo de toda la playa durante toda la temporada de anidación.La erosión es predominante en el frente de playa del sector oriental,desde mediados hasta finales de la época de anidación.Patrones similares de &quot;acreción &quot;y erosión fueron observados en el 2000.No hubo inundaciones durante el estudio o en el año anterior. Como hay zonas de alto riesgo y zonas estables,no hay evidencia contundente para hacer un criadero.</p></abstract>
<kwd-group>
<kwd>Leatherback turtle</kwd>
<kwd>beach dynamics</kwd>
<kwd>turtle nest distribution</kwd>
<kwd>community participation</kwd>
<kwd>Trinidad and Tobago</kwd>
<kwd>Baulas</kwd>
<kwd>dinámica de playa</kwd>
<kwd>distribución de nidos de tortugas</kwd>
<kwd>participación comunitaria</kwd>
<kwd>Trinidad y Tobago</kwd>
</kwd-group>
</article-meta>
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