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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420060006</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>S0034-77442006000600001</article-id>
<title-group>
<article-title xml:lang="en">Organizing Committee</article-title>
<article-title xml:lang="es">Comité organizador</article-title>
</title-group>
<aff id="A">
<institution>,  </institution>
<addr-line> </addr-line>
</aff>
<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
</pub-date>
<pub-date pub-type="epub">
<year>2006</year>
</pub-date>
<volume>54</volume>
<fpage>vii</fpage>
<lpage>vii</lpage>
<copyright-statement/>
<copyright-year/>
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</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">S0034-774420060006</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>S0034-77442006000600002</article-id>
<title-group>
<article-title xml:lang="en">Special Acknowledgement</article-title>
<article-title xml:lang="es">Agradecimiento especial</article-title>
</title-group>
<aff id="A">
<institution>,  </institution>
<addr-line> </addr-line>
</aff>
<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
</pub-date>
<pub-date pub-type="epub">
<year>2006</year>
</pub-date>
<volume>54</volume>
<fpage>viii</fpage>
<lpage>viii</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600002&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=S0034-77442006000600002&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=S0034-77442006000600002&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">S0034-774420060006</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>S0034-77442006000600003</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>12</month>
<year>2006</year>
</pub-date>
<pub-date pub-type="epub">
<year>2006</year>
</pub-date>
<volume>54</volume>
<fpage>ix</fpage>
<lpage>ix</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600003&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=S0034-77442006000600003&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=S0034-77442006000600003&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">S0034-774420060006</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>S0034-77442006000600004</article-id>
<title-group>
<article-title xml:lang="en">Program for the 32nd Scientific Meeting of the Association of Marine Laboratories of the Caribbean June 13 - 17, 2005</article-title>
</title-group>
<aff id="A">
<institution>,  </institution>
<addr-line> </addr-line>
</aff>
<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
</pub-date>
<pub-date pub-type="epub">
<year>2006</year>
</pub-date>
<volume>54</volume>
<fpage>xi</fpage>
<lpage>xi</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600004&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=S0034-77442006000600004&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=S0034-77442006000600004&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">S0034-774420060006</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>S0034-77442006000600005</article-id>
<title-group>
<article-title xml:lang="en">Posters for the 32nd Scientific Meeting of the Association of Marine Laboratories of the Caribbean June 13 - 17, 2005</article-title>
</title-group>
<aff id="A">
<institution>,  </institution>
<addr-line> </addr-line>
</aff>
<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
</pub-date>
<pub-date pub-type="epub">
<year>2006</year>
</pub-date>
<volume>54</volume>
<fpage>xix</fpage>
<lpage>xix</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600005&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=S0034-77442006000600005&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=S0034-77442006000600005&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">S0034-774420060006</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>S0034-77442006000600006</article-id>
<title-group>
<article-title xml:lang="en">New records of parasites for culture Cobia, Rachycentron canadum (Perciformes: Rachycentridae) in Puerto Rico</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
<name>
<surname>Bunkley-Williams</surname>
<given-names>Lucy</given-names>
</name>
<xref ref-type="aff" rid="A01"/>
</contrib>
<contrib contrib-type="author">
<name>
<surname>Williams, Jr.</surname>
<given-names>Ernest H</given-names>
</name>
<xref ref-type="aff" rid="A02"/>
</contrib>
</contrib-group>
<aff id="A01">
<institution>,University of Puerto Rico  </institution>
<addr-line> </addr-line>
<country>USA</country>
</aff>
<aff id="A02">
<institution>,University of Puerto Rico  </institution>
<addr-line> </addr-line>
<country>USA</country>
</aff>
<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
</pub-date>
<pub-date pub-type="epub">
<year>2006</year>
</pub-date>
<volume>54</volume>
<fpage>1</fpage>
<lpage>7</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600006&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=S0034-77442006000600006&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=S0034-77442006000600006&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Intensive aquaculture sometimes provides conditions favorable for parasites that are not ordinarily found on culture fishes in the wild, and the use of introduced stocks sometimes introduces non-indigenous species to the habitat. When officially asked about the culture of Cobia Rachycentron canadum (Linnaeus) in Puerto Rico, the authors responded that it was unlikely to cause harm. It was assumed that a well-known culture facility in Florida would assure parasite-free stocks. Subsequent examinations of stocked juveniles surprisingly found parasites new to this fish. An outbreak of Slime-blotch disease, Brooklynella hostilis Lom &amp; Nigrilli, 1970 (Dysteriida: Hartmannulidae) occurred in juvenile Cobia after they were shipped from Florida and stocked. This apparently represents a local parasite that took advantage of the weakened and/or crowded fish. The universal aquarium and culture superparasite, Marine Ich, Cryptocaryon irritans Brown, 1951 (Colpodia: Ichthyophthiriidae) was introduced with a shipment of juvenile Cobia from Florida. This may not be serious, since the parasite occurs worldwide, unless it represents a new strain to Puerto Rico. Marine Costia, Ichthyobodo sp. (Kinetoplastida: Bodonidae) was introduced into Puerto Rico with juvenile Cobia shipped from Florida. This parasite has caused some severe problems in aquaculture hatcheries in Hawaii and Texas after it was introduced with cultured organisms. Thus far, it has not caused any problems locally, but Puerto Rico lacks the marine hatchery facilities where such outbreaks would occur. The question of whether it is established locally will have to wait the development of similar facilities in Puerto Rico. These three species of parasites represent new host records for Cobia. The non-indigenous Ichthyobodo sp. represents new locality records for the tropical Atlantic, Caribbean, and Florida and Puerto Rico. Cobia mature more quickly in culture than in the wild and thus female Cobia apparently mature sufficiently before harvest to attract wild male Cobia to the net pen culture facilities. This represents a potential source of parasite and disease infection for the cultured and wild fish. Rev. Biol. Trop. 54 (Suppl. 3): 1-7. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>En un criadero del pez Rachycentron canadum establecido en Puerto Rico a partir de especímenes de Florida hallamos parásitos nuevos. La enfermedad causada por Brooklynella hostilis Lom and Nigrilli, 1970 (Dysteriida: Hartmannulidae) podría indicar que un parásito local tomó ventaja de los peces debilitados y/o hacinados. También hallamos Cryptocaryon irritans Brown, 1951 (Colpodia: Ichthyophthiriidae), parásito cosmopolita. También llegó de Florida Ichthyobodo sp. (Kinetoplastida: Bodonidae), el cual hasta ahora no ha causado ningún problema localmente, pero es un nuevo registro para el Atlántico tropical, el Caribe, Florida y Puerto Rico. Los tres parásitos son huéspedes nuevos de R. canadum. Aparentemente, antes de la cosecha las hembras maduran lo suficiente para atraer machos salvajes hacia los cultivos. Esto representa una potencial fuente de infección.</p></abstract>
<kwd-group>
<kwd>parasites</kwd>
<kwd>Cobia</kwd>
<kwd>Brooklynella hostili</kwd>
<kwd>Cryptocaryon irritans</kwd>
<kwd>Ichthyobodo sp.</kwd>
<kwd>Rachycentron canadum</kwd>
<kwd>parásitos</kwd>
<kwd>Cobia</kwd>
<kwd>Brooklynella hostilis</kwd>
<kwd>Cryptocaryon irritans</kwd>
<kwd>Ichthyobodo sp.</kwd>
<kwd>Rachycentron canadum</kwd>
</kwd-group>
</article-meta>
</front>
<back>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600007&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=S0034-77442006000600007&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=S0034-77442006000600007&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>An international team of scientists from government agencies and universities in the United States, U.S. Virgin Islands (USVI), Trinidad &amp; Tobago, the Republic of Cape Verde, and the Republic of Mali (West Africa) is working together to elucidate the role Saharan dust may play in the degradation of Caribbean ecosystems. The first step has been to identify and quantify the persistent organic pollutants (POPs), trace metals, and viable microorganisms in the atmosphere in dust source areas of West Africa, and in dust episodes at downwind sites in the eastern Atlantic (Cape Verde) and the Caribbean (USVI and Trinidad &amp; Tobago). Preliminary findings show that air samples from Mali contain a greater number of pesticides, polychlorinated biphenyls (PCBs) and polycyclic aromatic hydrocarbons (PAHs) and in higher concentrations than the Caribbean sites. Overall, POP concentrations were similar in USVI and Trinidad samples. Trace metal concentrations were found to be similar to crustal composition with slight enrichment of lead in Mali. To date, hundreds of cultureable micro-organisms have been identified from Mali, Cape Verde, USVI, and Trinidad air samples. The sea fan pathogen, Aspergillus sydowii, has been identified in soil from Mali and in air samples from dust events in the Caribbean. We have shown that air samples from a dust-source region contain orders of magnitude more cultureable micro-organisms per volume than air samples from dust events in the Caribbean, which in turn contain 3-to 4-fold more cultureable microbes than during non-dust conditions. Rev. Biol. Trop. 54 (Suppl. 3): 9-21. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Un grupo internacional de agencias gubernamentales y universidades de los Estados Unidos, las Islas Vírgenes (EUA), Trinidad y Tobago, la República de Cabo Verde y la República de Mali (África Oeste), está trabajando en conjunto para elucidar el papel que el polvo del Sahara puede estar jugando en el deterioro de los ecosistemas caribeños. El primer paso ha sido identificar y cuantificar los Contaminantes Orgánicos Persistentes (POPs, por sus siglas en inglés), los metales traza y los microorganismos viables presentes en la atmósfera de las áreas fuente de polvo de África occidental y en áreas ubicadas en la dirección del viento, como el Atlántico este (Cabo Verde) y el Caribe (IVEUA y Trinidad y Tobago), durante los episodios de transporte de polvo. Resultados preliminares indican que las muestras de aire de Mali contienen mayor número y mayores concentraciones de pesticidas, bifenilos policlorinados (PCBs) e hidrocarburos policíclicos aromáticos (PAHs) que las de los sitios del Caribe. Las concentraciones de POPs fueron similares en las muestras de USVI y de Trinidad. Se encontró que las concentraciones de metales traza fueron similares a las de la composición de la corteza, con un ligero enriquecimiento de plomo en Mali. Hasta la fecha, cientos de microorganismos cultivables han sido identificados en las muestras de Mali, Cabo Verde, IVEUA y Trinidad. Hallamos el patógeno de los abanicos de mar, Aspergillus sydowi, en las muestras de aire de Mali y en las muestras del Caribe durante polvaredas. Hemos demostrado que las muestras de aire provenientes de una región fuente de polvo, contienen más microorganismos cultivables por volumen -en órdenes de magnitud- que las muestras de aire tomadas en polvaredas en el Caribe, las cuales a su vez contienen tres a cuatro veces más microorganismos cultivables que aquellas tomadas cuando no hay polvaredas.</p></abstract>
<kwd-group>
<kwd>African dust</kwd>
<kwd>Caribbean</kwd>
<kwd>coral pathogens</kwd>
<kwd>persistent organic pollutants</kwd>
<kwd>Saharan dust</kwd>
<kwd>polvo africano</kwd>
<kwd>Caribe</kwd>
<kwd>patógenos de corales</kwd>
<kwd>contaminantes orgánicos persistentes</kwd>
<kwd>polvo del Sahara</kwd>
</kwd-group>
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<journal-id pub-id-type="pid">S0034-774420060006</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
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<title-group>
<article-title xml:lang="en">A vision for regular, rapid assessments of the tropical northwestern Atlantic’s coral reefs</article-title>
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<institution>,Ophelia  </institution>
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<institution>,University of Miami  </institution>
<addr-line> Florida</addr-line>
<country>USA</country>
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<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600008&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=S0034-77442006000600008&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=S0034-77442006000600008&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The Atlantic and Gulf Rapid Reef Assessment (AGRRA) Program, consisting of non-fixed, transect- based visual surveys, provides &quot;snapshot&quot; characterizations of a number of structurally or functionally important benthic and fish indicators on tropical northwestern Atlantic (TNWA) coral reefs and Brazil. To ameliorate the confounding factors inherent in multiyear temporal variation, a region-wide collaborative program for conducting rapid reef assessments at regular (five-year) intervals in sites that are representative of each sub-region of the TNWA is proposed. Member institutions of the Association of Marine Laboratories of the Caribbean (AMLC) and individual colleagues are invited to join in developing the vision. Rev. Biol. Trop. 54 (Suppl. 3): 23-29. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El Programa de Evaluación Rápida del Atlántico y el Golfo (AGRRA, por sus siglas en inglés) consiste en sondeos visuales no-fijos, basados en transectos, que permiten caracterizaciones puntuales de un número de peces y organismos bénticos que sean estructural o funcionalmente importantes como indicadores en arrecifes del Atlántico tropical noroeste (ATNO) y de Brasil. Para disminuir los factores de confusión inherentes a variaciones temporales multianuales, se propone un programa de colaboración a nivel regional, que sirva para conducir evaluaciones rápidas de los arrecifes en intervalos regulares (cinco años), en los sitios que sean representativos de cada sub-región del ATNO. Se invita a las instituciones miembro de la Asociación de Laboratorios Marinos y del Caribe (ALMC), así cómo a colegas individuales para participar en el desarrollo de esta visión.</p></abstract>
<kwd-group>
<kwd>coral reefs</kwd>
<kwd>rapid assessment</kwd>
<kwd>AGRRA</kwd>
<kwd>AMLC</kwd>
<kwd>long-term monitoring</kwd>
<kwd>monitoring</kwd>
<kwd>coral reef integrity</kwd>
<kwd>arrecifes de coral</kwd>
<kwd>evaluación rápida</kwd>
<kwd>AGRRA</kwd>
<kwd>AMLC</kwd>
<kwd>monitoreo a largo plazo</kwd>
<kwd>monitoreo</kwd>
<kwd>integridad de los arrecifes de coral</kwd>
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<title-group>
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<fpage>31</fpage>
<lpage>43</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600009&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=S0034-77442006000600009&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=S0034-77442006000600009&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Chronic anthropogenic impacts can have a negative effect on coral health and on coral energy budgets needed for regeneration of lesions. I therefore hypothesise that during massive bleaching events, the degree of corals showing bleaching-related tissue mortality is higher in areas subject to chronic anthropogenic impacts than in relatively pristine areas. In the present study, the degree of bleaching and bleaching-related tissue mortality was estimated for eight abundant coral species in Curaçao, at the onset of a massive Caribbean bleaching event in 1995, and three months afterwards. To study the possible effects of anthropogenic disturbances, the study was done at four unpolluted control sites, two polluted sites (sedimentation, sewage), and four sites at the mouth of lagoons with outflow of nutrient-rich, warm and turbid seawater. No pattern of an overall difference in bleaching between impacted and control sites was found for the degree of bleaching. However, the percentage of corals showing bleaching-related tissue mortality was higher at the impacted sites than at the control sites for the total number of corals and for corals with &lt; 50% of their surface area bleached. Highest and most significant values of tissue mortality were found at a reef site experiencing chronic pollution by raw sewage. The data thus suggest that unfavourable conditions caused by anthropogenic influences, such as increased sedimentation, eutrophication and seawater temperature, have an additional negative effect on the tissue survival of coral colonies during bleaching episodes. Rev. Biol. Trop. 54 (Suppl. 3): 31-43. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Los impactos antropogénicos crónicos pueden tener efectos negativos en la salud y en las cantidades de energía necesarias para la regeneración de lesiones en los corales. Mi hipótesis fue que durante los casos de blanqueamiento masivo, el grado en que los corales muestren mortalidades de tejido relacionadas con el blanqueamiento, será mayor en áreas sujetas a impactos antropogénicos crónicos que en áreas relativamente prístinas. Estimé los grados de blanqueamiento y mortalidad tisular en ocho especies de coral abundantes en Curaçao, durante el comienzo de un de blanqueamiento masivo en el Caribe en 1995 y tres meses después. El estudio se realizó en cuatro sitios control no contaminados, dos sitios contaminados (sedimentación, aguas residuales), y cuatro sitios en la boca de lagunas con aguas tibias, ricas en nutrientes y turbias. En general, no se encontró ningún patrónx de diferencias en el grado de blanqueamiento entre sitios. Sin embargo, el porcentaje de corales que mostraron mortalidad tisular relacionada con el blanqueamiento fue mayor en los sitios impactados que en los controles, tanto en el número total de corales como en corales con &lt;50% de su superficie blanquedada. Los valores más altos y más significativos de mortalidad tisular se encontraron en un arrecife que experimentaba contaminación crónica por aguas residuales crudas. La información sugiere que las condiciones desfavorables causadas por la influencia antropogénica, como el incremento en la sedimentación, eutrofización y la temperatura del agua, tienen un efecto negativo adicional en la supervivencia del tejido de las colonias de coral, durante el blanqueamiento.</p></abstract>
<kwd-group>
<kwd>Stony corals</kwd>
<kwd>bleaching</kwd>
<kwd>tissue mortality</kwd>
<kwd>anthropogenic impacts</kwd>
<kwd>Caribbean</kwd>
<kwd>corales pétreos</kwd>
<kwd>blanqueamiento</kwd>
<kwd>mortalidad tisular</kwd>
<kwd>impactos antropogénicos</kwd>
<kwd>Caribe</kwd>
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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420060006</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>S0034-77442006000600010</article-id>
<title-group>
<article-title xml:lang="en">The recent decline of Montastraea annularis (complex) coral populations in western Curaçao: a cause for concern?</article-title>
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<aff id="A01">
<institution>,Office of Habitat Conservation  </institution>
<addr-line> </addr-line>
<country>USA</country>
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<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
</pub-date>
<pub-date pub-type="epub">
<year>2006</year>
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<volume>54</volume>
<fpage>45</fpage>
<lpage>58</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600010&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=S0034-77442006000600010&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=S0034-77442006000600010&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Shallow leeward reefs off the western end of Curaçao are dominated by extensive populations of M. annularis (complex). These species are larger in size (mean= 66 cm diameter) than all other species, with few small colonies (&amp;lt;30 cm) and notable absence of recruits. In 1998, colonies of M. annularis (complex) accounted for more then 45% of all species &gt;10 cm observed within transects, and most exhibited low levels of partial mortality (mean= 22.5%). These species were less abundant (38% of all colonies) in 2005. Partial mortality among live colonies of M. annularis and M. faveolata increased by 85% (mean = 42% partial mortality) and numerous dead colonies of M. faveolata and M. annularis were observed; M. franksi colonies were generally in excellent condition (14% partial tissue mortality). A high prevalence of coral diseases (3-30%) was documented among M. annularis and M. faveolata, while all other species were less frequently affected. Yellow band disease (YBD) emerged shortly after the 1995 bleaching event, and rapidly spread throughout all depths, with the highest prevalence between 1997-1999. YBD caused slow rates of mortality (=1 cm/month), but multiple focal lesions appeared on individual colonies, and these progressively radiated outward as they killed the colonies. By 2005, 44% of the tagged corals were dead; the remainder exhibited active YBD infections (21%) or were in remission (31.6%) but were missing on average &gt;90% of their tissue. Although the incidence of YBD has declined since 2000, white plague (WP) prevalence was unusually high (4-12%) in 2001 and 2005, with affected colonies exhibiting recent mortality of up to 70%. Dead Montastraea spp. surfaces are being colonized by other corals, including poritids, agaricids, and other faviids, while recruits of M. annularis (complex) are absent. If diseases and other biotic stressors persist on these reefs, M. annularis and M. faveolata populations may undergo a decline similar to that observed in the 1980s among Caribbean acroporids. Rev. Biol. Trop. 54 (Suppl. 3): 45- 58. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Los arrecifes someros a sotavento del oeste de Curaçao están dominados por extensas poblaciones de Montastraea annularis (complejo). Estas especies son mayores en tamaño (promedio= 66 cm de diámetro) que las otras especies, con algunas colonias pequeñas (&amp;lt;30 cm) y una notable ausencia de reclutas. En 1998, las colonias de Montastraea annularis (complejo), representaban más del 45% de todas las especies de &gt;10 cm observadas en transectos y la mayoría exhibió bajos niveles de mortalidad parcial (prom= 22.5%). En el 2005, fueron menos abundantes (38% de las colonias). La mortalidad parcial en colonias vivas de M. annularis y M. faveolata se incrementó en un 85% (promedio= 42% de mortalidad parcial) y se observaron numerosas colonias de M. annularis y M. faveolata muertas; las colonias de M. franski generalmente se encontraron en excelentes condiciones (14% de mortalidad parcial). Se documentó una alta prevalencia de enfermedades de coral (3-30%) en M. annularis y M. faveolata, mientras que las otras especies se vieron afectadas con menor frecuencia. La enfermedad de banda amarilla (BA) emergió poco después del blanqueamiento de 1995 y se dispersó rápidamente en todas las profundidades, alcanzando su mayor prevalencia entre 1997-1999. La BA causó mortalidades lentas (= 1cm/mes), con aparición de múltiples lesiones focales en colonias individuales; estas lesiones fueron creciendo progresivamente al tiempo que mataban las colonias. Para el año 2005, el 44% de los corales que se etiquetaron habían muerto; los restantes exhibían infecciones activas de BA (21%), o estaban en remisión (31.6%) pero habían perdido un promedio de &gt;90% de su tejido. Aunque la incidencia de BA disminuyó a partir del 2000, la prevalencia de la plaga blanca (PB) fue inusualmente alta (4-12%) en el 2001 y 2005, provocando mortalidades recientes de hasta un 70% en las colonias afectadas. Las superficies muertas de Montastraea spp. han sido colonizadas por otros corales, incluyendo porítidos, agarícidos y otros fávidos, mientras que continúa la ausencia de reclutas de M. annularis (complejo). Si las enfermedades y otros estresores bióticos persisten en estos arrecifes, las poblaciones de M. annularis y M. faveolata podrían decaer de forma similar a como lo hicieron los acropóridos del Caribe durante la década de 1980.</p></abstract>
<kwd-group>
<kwd>coral monitoring</kwd>
<kwd>coral disease</kwd>
<kwd>yellow-band disease</kwd>
<kwd>white plague</kwd>
<kwd>star coral</kwd>
<kwd>Montastraea annularis (complex)</kwd>
<kwd>Curaçao</kwd>
<kwd>Caribbean</kwd>
<kwd>monitoreo de corales</kwd>
<kwd>enfermedad de corales</kwd>
<kwd>enfermedad de banda amarilla</kwd>
<kwd>plaga blanca</kwd>
<kwd>coral estrella</kwd>
<kwd>Montastraea annularis (complejo)</kwd>
<kwd>Curaçao</kwd>
<kwd>Caribe</kwd>
</kwd-group>
</article-meta>
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<article-id>S0034-77442006000600011</article-id>
<title-group>
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<institution>,Instituto de Investigaciones Marinas y Costeras INVEMAR  </institution>
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<country>Colombia</country>
</aff>
<aff id="A02">
<institution>,University of South Carolina Aiken  </institution>
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<country>USA</country>
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<aff id="A03">
<institution>,University of Puerto Rico  </institution>
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<country>Puerto Rico</country>
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<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
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<volume>54</volume>
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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=S0034-77442006000600011&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=S0034-77442006000600011&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=S0034-77442006000600011&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The white band disease type I (WBD-I) epizootic event of the early 1980’s resulted in significant changes in the structure and composition of coral communities throughout the wider Caribbean. The disease decimated populations of acroporid corals throughout their geographic distribution and it is still affecting the surviving and recovering populations of these corals in a number of localities in the wider Caribbean. The putative pathogen for this syndrome (WBD-I) was never identified. A second pattern of white band was described later as white band type II (WBD-II). A potential pathogen named Vibrio charchariae was identified but Koch’s postulates were never fulfilled. In this work, we present results of a preliminary approach to confirm the identity of the pathogen of WBD-II. During the fall months of 2004, samples of Acropora cervicornis with signs of WBD-II were collected from a small population in Mario reef, an isolated patch reef off La Parguera, southwest coast of Puerto Rico. Bacteria extracted from these samples were isolated in TCBS agar, grown in Glycerol Seawater agar, and then used to inoculate separated, healthy-looking colonies of the same population in the same reef. Isolation, culture, and inoculations of bacteria were conducted under controlled conditions within hours of collection, and no microorganisms that were not already in the reef community were introduced with these experiments. Some of the newly inoculated colonies developed the disease signs within 24 hr. These were subsequently sampled and bacterial re-isolated to be identified, thus complying with the first steps to fulfill Koch ’s postulates for this disease. Rates of advance of the disease signs varied between 0.5 and 2 cm/day. Preliminary analyses indicated that the potential cause of WBD-II is a Vibrio species very close to Vibrio harveyi, a synonymy of V. charchariae. All inoculated coral colonies that developed the signs of WBD-II, behaved as the naturally infected colonies, and all of them showed no signs of the disease after two months of the inoculation when water temperatures dropped due to winter in the area. Rev. Biol. Trop. 54 (Suppl. 3): 59-67. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El evento epizoótico de la enfermedad de banda blanca tipo I (WBD-I) al principio del decenio de 1980 causó cambios significativos en la composición de las comunidades coralinas a todo lo largo del Gran Caribe. La enfermedad eliminó altas proporciones de las poblaciones de acropóridos y aún hoy continua afectando la recuperación de sus poblaciones en muchas localidades. El agente causante de esta enfermedad (WBD-I) nunca fue identificado. Un conjunto de características diferentes de esta enfermedad fue descrito en 1998, como banda blanca tipo II (WBD-II), y la bacteria Vibrio charchariae fue identificada como la posible causante. Sin embargo, los postulados de Koch nunca se cumplieron. En este trabajo presentamos los resultados de estudios preliminares para identificar el agente causante de WBD-II en el Caribe. Durante los meses de otoño del 2003 y 2004, recolectamos muestras de Acropora cervicornis con signos de WBD-II en Mario, un arrecife de parche aislado en La Parguera, costa sur occidental de Puerto Rico. Las bacterias extraídas de estas muestras fueron aisladas en agar TCBS, criadas en agar Glicerol Agua de mar y luego utilizadas para infectar colonias separadas sin signos de enfermedad en la misma población y localidad. El aislamiento, cultivo e inoculación de bacterias se hizo en condiciones controladas, y no introdujimos ningún microorganismo que no hubiera estado previamente en el arrecife. Algunas de las colonias inoculadas desarrollaron signos de la enfermedad en 24 hr. Tomamos muestras de estas colonias y las bacterias fueron nuevamente aisladas para ser identificadas y así completar los postulados de Koch. Las tasas de avance de los signos de la enfermedad variaron entre 0.5 y 2 cm/día. Preliminarmente confirmamos que la causa de WBD-II es una especie de Vibrio muy cercana a Vibrio harveyi, sinónimo de V. charchariae. Todas las colonias coralinas inoculadas que desarrollaron signos de WBD-II se comportaron como las colonias infectadas naturalmente y ninguna de ellas presentó signos de la enfermedad al cabo de dos meses, cuando las temperaturas del agua descendieron con el invierno.</p></abstract>
<kwd-group>
<kwd>White Band Disease Type II</kwd>
<kwd>Acropora cervicornis</kwd>
<kwd>Vibrio harveyi</kwd>
<kwd>Vibrio charchariae</kwd>
<kwd>Koch’s postulates</kwd>
<kwd>field Inoculations</kwd>
<kwd>Enfermedad de Banda Blanca Tipo II</kwd>
<kwd>Acropora cervicornis</kwd>
<kwd>Vibrio harveyi</kwd>
<kwd>Vibrio charchariae</kwd>
<kwd>postulados de Koch</kwd>
<kwd>inoculación en el campo</kwd>
</kwd-group>
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<title-group>
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<institution>,University of the Virgin Islands  </institution>
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<year>2006</year>
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<volume>54</volume>
<fpage>69</fpage>
<lpage>78</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600012&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=S0034-77442006000600012&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=S0034-77442006000600012&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The Grammanik bank is a deep reef (35-40 m) located approximately 14 km south of St. Thomas USVI, on the southern edge of the Puerto Rico shelf. The relatively narrow 1.5 km long reef annually hosts spawning aggregations of several species of groupers, snappers and jacks. Until February of 2005, when temporary seasonal protection was offered by the Caribbean Fisheries Management Council, the bank was subject to moderate or heavy exploitation from fishers. Cubera snapper (Lutjanus cyanopterus) were observed aggregating on the Grammanik bank in relatively large numbers from 2003 to 2005 and dog snapper (L. jocu) aggregations were observed in 2005. The arrival and departure of these aggregations appeared to be seasonal and to revolve around the moon phase. Cubera snapper spawning seasonality coincided with that elsewhere in the Caribbean and off south Florida. Schools of up to 1000 fish of each species were observed as well as pre-spawning behavior and milt release. Aggregations of both species showed high site fidelity within seasons but cubera snapper aggregations sites moved between seasons. The authors recommend year-round closure of the Grammanik bank based on its importance as critical fish habitat and a multi-species aggregation area. Rev. Biol. Trop. 54 (Suppl. 3): 69-78. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El banco Grammanik es un arrecife profundo (35-40 m) ubicado aproximadamente 14 km al Sur de St. Thomas (Islas Vírgenes EUA), en el límite sur de la plataforma de Puerto Rico. Este arrecife relativamente angosto y de 1.5 km de longitud, recibe anualmente agrupaciones de varias especies de meros, pargos y jureles, durante sus desoves. Fue objeto de explotación de moderada a alta por parte de los pescadores hasta febrero del 2005, cuando el Consejo de Pesca del Caribe le ofreció protección temporal. El pargo cubera (Lutjanus cyanopterus) fue observado en el banco Grammanik en agrupaciones numerosas entre el año 2003 y el 2005, a su vez, agrupaciones del pargo perro o pargo caucha (L. jocu) se observaron en el 2005. La llegada y partida de estos grupos parece ser estacional y estar relacionada con la fase lunar. El desove estacional del pargo cubera coincide con informes de otros sitios del Caribe y al Sur de la Florida, donde se observaron cardúmenes de hasta 1000 peces de cada especie, así como comportamientos previos al desove y liberación de esperma. Agrupaciones de ambas especies mostraron alta fidelidad al sitio en una misma estación, pero los sitios de agrupación del pargo cubera cambiaron entre estaciones. Los autores recomiendan el cierre del banco Gammanik durante todo el año, basados en su importancia como hábitat crítico para los peces y por ser un área de agrupación para múltiples especies.</p></abstract>
<kwd-group>
<kwd>spawning aggregations</kwd>
<kwd>cubera snapper</kwd>
<kwd>dog snapper</kwd>
<kwd>Lutjanidae</kwd>
<kwd>MPA</kwd>
<kwd>agrupaciones de desove</kwd>
<kwd>pargo cubera</kwd>
<kwd>pargo perro o caucha</kwd>
<kwd>Lutjanidae</kwd>
<kwd>Áreas Marinas Protegidas (AMP)</kwd>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600013&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=S0034-77442006000600013&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=S0034-77442006000600013&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Coral bleaching involves the detachment of zooxanthellae and the simultaneous fragmentation of the gastrodermis. Results obtained with a cell permeant fluorescent probe for calcium ions (Ca2+) indicates that &quot;thermal&quot; bleaching is the result of a temperature related breakdown of the Ca2+ exclusion system. &quot;Solar&quot; bleaching, which takes place at lower temperatures and is driven by light, is the result of a build-up of photo-synthetically produced hydrogen peroxide in the tissues. Gastrodermal tissue with its symbionts, scraped from between septa of corals, was observed under controlled conditions of high light and temperature. Pieces of gastrodermis round off, zooxanthellae move to the surface, protrude from the surface and after a delay, detach, surrounded by a thin layer of host cytoplasm, inclusions and plasma membrane. The higher the temperature and light level the shorter the delay and higher the rate of algal detachment. Fragmentation by the ballooning-out and detachment of small spheres of cytoplasm (bleb formation) takes place simultaneously. This is likely to be due to oxidation, by hydrogen peroxide (H2O2), of -SH groups on the cytoskeleton and its attachment to the plasma membrane. Ground, polished and stained thin acrylic resin sections reveal similar processes taking place in artificially bleached corals. Isolated zooxanthellae and whole corals are shown to release H2O2 in the light. This process of algal detachment and fragmentation that takes place at normal sea temperatures may underlie the mechanism limiting algal populations in the gastrodermis and may be localized to areas with a concentration of algae near the membrane. At above-normal temperatures under the synergistic effect of light and temperature, the rate of production of H2O2 exceeds the rate at which can it be lost by diffusion or destroyed and H2O2 accumulates. This results in damage to the calcium exclusion system, detachment of zooxanthellae into the coelenteron and fragmentation of the gastrodermis. Rev. Biol. Trop. 54 (Suppl. 3): 79-96. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>El blanqueamiento de los corales implica el desprendimiento de zooxantelas y la simultánea fragmentación de la gastrodermis. Resultados obtenidos con una sonda florescente de iones Calcio (Ca2+) para células permeables, indican que el blanqueamiento &quot;térmico&quot; es el resultado de una interrupción del sistema de exclusión de Ca2+, provocada por la temperatura. El blanqueamiento &quot;solar&quot;, que tiene lugar a temperaturas más bajas y está determinado por la luz, es el resultado de una acumulación de peróxido de hidrógeno producido fotosintéticamente en los tejidos. Para ver el proceso, se raspó tejido gastrodermal, junto con sus simbiontes, de entre los septos de los corales y se observó en condiciones controladas de luz y temperatura. Primero, los trozos de gastrodermis se dan vuelta, luego las zooxantelas se mueven hacia la superficie, sobresalen desde ella y tras un tiempo, se desprenden, rodeadas de una delgada capa de citoplasma del hospedero, inclusiones y membrana plasmática. Mientras mayor sea la temperatura y el nivel de luz, menor es el tiempo que tardan las zooxantelas en desprenderse y mayor es la tasa de desprendimiento algal. La fragmentación producida por el inflamación y el desprendimiento de pequeñas esferas de citoplasma (formación de ampollas), tiene lugar simultáneamente. Probablemente, esto es causado por oxidación en el citoesqueleto de grupos -SSH por el peróxido de hidrógeno (H2O2), y por su acoplamiento a la membrana plasmática. Secciones de resina acrílica delgada molida, pulida y teñida revelan que en corales blanqueados artificialmente se llevan a cabo procesos similares. Se ha demostrado que tanto las zooxantelas aisladas como los corales enteros, liberan H2O2 en la luz. Debajo este proceso de desprendimiento algal y fragmentación que tiene lugar a temperaturas normales en el mar, puede encontrarse el mecanismo que limita las poblaciones algales en la gastrodermis, el cual podría estar localizado en áreas con concentraciones de alga cerca de la membrana. A temperaturas más altas de lo normal, bajo el efecto sinérgico de la luz y la temperatura, la tasa de producción de H2O2 excede la tasa a la cual éste puede destruirse o perderse por difusión y, por ende,se acumula. Esto resulta en daño al sistema de exclusión de calcio, desprendimiento de zooxantelas hacia el celenterón y fragmentación de la gastrodermis.</p></abstract>
<kwd-group>
<kwd>Zooxanthellae</kwd>
<kwd>coral bleaching</kwd>
<kwd>Hydrogen peroxide</kwd>
<kwd>Ca2+</kwd>
<kwd>algal density</kwd>
<kwd>algal detachment</kwd>
<kwd>gastrodermal fragmentation</kwd>
<kwd>zooxantela</kwd>
<kwd>blanquamiento de corales</kwd>
<kwd>peróxido de hidrógeno</kwd>
<kwd>Ca2+</kwd>
<kwd>densidad algal</kwd>
<kwd>desprendimiento algal</kwd>
<kwd>fragmentación gastrodermal</kwd>
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<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
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<article-id>S0034-77442006000600014</article-id>
<title-group>
<article-title xml:lang="en">A recent increase in the abundance of the echinoid Diadema antillarum in Dominica (Lesser Antilles): 2001-2005</article-title>
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<aff id="A01">
<institution>,Institute for Tropical Marine Ecology Inc. (ITME)  </institution>
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<aff id="A02">
<institution>,University of Puerto Rico  </institution>
<addr-line> </addr-line>
<country>USA</country>
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<pub-date pub-type="pub">
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<lpage>103</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600014&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=S0034-77442006000600014&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=S0034-77442006000600014&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Diadema antillarum populations at many Caribbean locations have failed to recover from the pathogen-induced mortality events of the 1980s. It has become clear that the massive decline of this herbivorous urchin and the wide-spread absence of a population recovery lead to numerous long-term ecological consequences and reef degradation. While few quantitative studies on pre-mortality exist, great effort has been put forth to monitor remaining populations and their recovery. However, the patchy distribution of D. antillarum coupled with paucity of long-term studies based on the same methods applied at the same locations undermines the value of local as well as regional comparisons. In Dominica, ongoing quantitative assessments of D. antillarum began in 2001. Surveys of D. antillarum abundance are being carried out in 4-month intervals at six 100 m² sites; spread over 38 km along the west coast. The density of D. antillarum has differed significantly between sites, ranging from 0.81(SD= 0.04) to 3.13 m-2 (SD= 2.10), and increased by 61.11% during the first five years of this study. Seasonal fluctuations, possibly related to spawning aggregations, are also evident. The current abundance of D. antillarum on Dominican reefs contrasts that of Caribbean locations with recorded incidents of mass mortality events, and in some cases resembles pre-mortality densities from the early 1970s. Prior to this study, no systematic quantitative assessments of D. antillarum were carried out in Dominica. It is thus unclear in what way Dominica’s D. antillarum were affected by the mass mortality events observed elsewhere in the 1980s. The increase in D. antillarum density so far observed may thus be the recovery from a pathogen-induced disturbance or from Hurricane Lenny in November 1999. Locally, D. antillarum is important grazer on Dominican’s reefs, where over-fishing has drastically reduced the number of herbivorous fishes. On a regional scale, the island’s D. antillarum may represent a source of larvae for downstream islands, given the duration of the echinoplutei stage and a range of larval dispersal of hundreds of kilometers. Rev. Biol. Trop. 54 (Suppl. 3): 97-103. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Las poblaciones de Diadema antillarum de muchas localidades del Caribe, no se han recuperado después de los eventos de mortandad, inducidos por un patógeno, en la década de 1980. Se ha podido demostrar que la muerte masiva de este erizo herbívoro y la ausencia de recuperación, han tenido consecuencias ecológicas que han producido la degradación de los arrecifes. Existen pocos estudios pre-mortalidad, pero se han realizado grandes esfuerzos para monitorear las poblaciones restantes y su recuperación. Sin embargo, la distribución en parches de D. antillarum combinado con pocos estudios a largo plazo usando la misma metodología en los mismos sitios, mina la posibilidad de comparaciones locales y regionales. En Dominica, el monitoreo cuantitativo de D. antillarum empezó en 2001. Cada cuatro meses se realizan determinaciones de abundancia de D. antillarum en seis sitios de 100 m²; distribuidos a lo largo de 38 km de la costa oeste. La densidad de D. antillarum, fue significativamente diferente entre sitios, con ámbitos de 0.81 (SD= 0.04) a 3.13 m-2 (SD= 2.10), y aumentó 61.11% durante los primeros cinco años de estudio. Fluctuaciones estacionales, posiblemente relacionadas con agregaciones reproductivas, son evidentes. La abundancia actual de D. antillarum en los arrecifes de Dominica contrasta con otros sitios en el Caribe que sufrieron mortandades masivas y en algunos casos se parece a densidades pre-mortalidad de inicios de la década de 1970. Antes de este trabajo, no se había realizado ningún estudio sistemático de Diadema en Dominica, por lo que no es claro como fueron afectadas las poblaciones en este sitio. El aumento en la densidad de D. antillarum observado hasta ahora puede deberse a recuperación tras una perturbación por un patógeno o por el Huracán Lenny de noviembre 1999. Localmente, D. antillarum es un herbívoro importante en los arrecifes de Dominica donde la sobrepesca ha disminuido el número de peces herbívoros. En escala regional, las poblaciones de D. antillarum de la isla de Dominica pueden representar una fuente de larvas corriente abajo, dada la duración de estadio equiinopluteo y el ámbito de dispersión de las larvas, que es de cientos de kilómetros.</p></abstract>
<kwd-group>
<kwd>Diadema antillarum</kwd>
<kwd>population density</kwd>
<kwd>Dominica</kwd>
<kwd>Lesser Antilles</kwd>
<kwd>Caribbean</kwd>
<kwd>Diadema antillarum</kwd>
<kwd>densidad poblacional</kwd>
<kwd>Dominica</kwd>
<kwd>Antillas menores</kwd>
<kwd>Caribe</kwd>
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<aff id="A01">
<institution>,University of the West Indies  </institution>
<addr-line>St. Ann </addr-line>
<country>Jamaica</country>
</aff>
<aff id="A02">
<institution>,Division of Fish and Wildlife  </institution>
<addr-line> </addr-line>
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<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
</pub-date>
<pub-date pub-type="epub">
<year>2006</year>
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<volume>54</volume>
<fpage>105</fpage>
<lpage>116</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600015&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=S0034-77442006000600015&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=S0034-77442006000600015&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Shallow water Acropora species have become uncommon on north coast Jamaican coral reefs owing to a number of factors. On many reefs, algae have taken their place. The result is loss of habitat for many species of fish and invertebrates and less attractive reefs with fewer fish. These reefs appear to be prime candidates for coral restoration. However, the potential for coral to naturally recover should be examined before efforts to restore reefs are undertaken. Reef restoration is unnecessary if the population has the capacity to recovery through natural means. We observed that the rate of settlement of Acropora spat in the Caribbean is much lower than the spat settlement rate of several other Caribbean coral families and much lower than Acropora spat settlement rates in the South Pacific. A very low percentage of apparently healthy colonies of A. cervicornis possessed developing gametes in July 2005, a month before spawning. It appears that the long-term survival of remnant A. cervicornis populations is threatened unless successful sexual reproduction is restored. Several techniques were used to test transplant methods for restoring A. cervicornis populations. The mean survivorship and growth rate of one technique was &gt;75% and nearly 250% per annum, respectively. Working with hotel operators, environmental groups, and local fishers, we are attempting to reintroduce A. cervicornis to sites where it previously existed and increase coral biomass and complexity at these sites. Reefs with greater A. cervicornis biomass have larger edible fish populations. With localized protection of these restored reefs we anticipate an increase of larger edible fish not only on reefs within the restored protected areas but also on adjacent reefs. Furthermore, increased coral and fish biodiversity improves the attractiveness of the reef community for divers and snorkelers. Rev. Biol. Trop. 54 (Suppl. 3): 105-116. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Las especies someras de Acropora se han vuelto poco comunes en los arrecifes de la costa norte de Jamaica debido a numerosos factores. En muchos arrecifes, las algas han tomado su lugar y el resultado es la pérdida de hábitat para muchas especies de peces e invertebrados y la pérdida de atractivo de los arrecifes, que tienen mucho menos peces. Estos arrecifes parecen ser excelentes candidatos para restauración de corales. Sin embargo, antes de emprender un esfuerzo de restauración, debe examinarse el potencial de los corales para regenerarse naturalmente, ya que si la población tiene la capacidad de recobrarse por sus propios medios, la restauración de arrecifes se vuelve innecesaria. Nosotros observamos que la tasa de colonización por adherencia a un sustrato duro de Acropora en el Caribe, es más baja que la de muchas otras familias de corales del Caribe y mucho menor que la de Acropora en el Pacífico sur. Un muy bajo porcentaje de colonias de A. cervicornis poseía gametos en desarrollo y estaba saludable en julio de 2005, un mes antes del desove. Al parecer, la supervivencia a largo plazo de las poblaciones remanentes de A. cervicornis está amenazada a menos que se restaure una reproducción sexual exitosa. Se utilizaron varias técnicas para probar los métodos de transplante para restaurar las poblaciones de A. cervicornis. La supervivencia promedio y la tasa de crecimiento resultantes de una de las técnicas fue de &gt;75% y de casi 250% por año, respectivamente. Al trabajar con agentes de hoteles, grupos ambientalistas y pescadores locales, estamos tratando de reintroducir A. cervicornis en lugares donde anteriormente existía e incrementar la biomasa del coral y la complejidad de estos sitios. Los arrecifes con mayores biomasas de A. cervicornis tienen también mayores poblaciones de peces comestibles. Si se protegen estos arrecifes en restauración, prevemos que habrá un incremento de peces comestibles, no sólo en los arrecifes restaurados, sino también en los adyacentes. Más aún, el aumento en la biodiversidad de corales y peces mejora el atractivo del arrecife para los buzos.</p></abstract>
<kwd-group>
<kwd>coral reefs</kwd>
<kwd>coral restoration</kwd>
<kwd>reproduction</kwd>
<kwd>Jamaica</kwd>
<kwd>Caribbean</kwd>
<kwd>arrecifes de coral</kwd>
<kwd>restauración de corales</kwd>
<kwd>reproducción</kwd>
<kwd>Jamaica</kwd>
<kwd>Caribe</kwd>
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<journal-title>Revista de Biología Tropical</journal-title>
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<article-id>S0034-77442006000600016</article-id>
<title-group>
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<institution>,Universidad de Oriente  </institution>
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<country>Venezuela</country>
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<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600016&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=S0034-77442006000600016&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=S0034-77442006000600016&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>A case of bilateral cheliped hypertrophya crab Uca cumulanta (Decapoda: Ocypodidae). An adult male of Uca cumulanta with bilateral cheliped hypertrophy was found during a collection of crabs at La Restinga Lagoon, Margarita Island, Venezuela. Both chelipeds were sub equal in size, regarding the major cheliped of a normal male. Rev. Biol. Trop. 54 (Suppl. 3): 117-119. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Un macho de Uca cumulanta con hipertrofia bilateral de quelas fue capturado durante en la Laguna de La Restinga, Isla de Margarita, Venezuela. Ambas quelas eran subiguales en tamaño y se asemejaban al quelípedo mayor de los machos normales.</p></abstract>
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<kwd>malformación</kwd>
<kwd>hipertrofia</kwd>
<kwd>cangrejos</kwd>
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<journal-id pub-id-type="pid">S0034-774420060006</journal-id>
<journal-title>Revista de Biología Tropical</journal-title>
<abbrev-journal-title>Rev. biol. trop</abbrev-journal-title>
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<article-id>S0034-77442006000600017</article-id>
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<article-title xml:lang="es">Estructura de la comunidad de moluscos y relaciones tróficas en el litoral rocoso del estado Sucre, Venezuela</article-title>
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<aff id="A02">
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<month>12</month>
<year>2006</year>
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<pub-date pub-type="epub">
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<fpage>121</fpage>
<lpage>130</lpage>
<copyright-statement/>
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<abstract abstract-type="short" xml:lang="es"><p>Se analizó la estructura de la comunidad de moluscos y sus relaciones tróficas en seis localidades del litoral rocoso con diferentes grados de exposición al oleaje (área expuesta y área protegida), en el Estado Sucre, Venezuela. El muestreo se llevó a cabo durante el período de marzo 2003 a febrero 2004. La recolección del material biológico se realizó de forma manual con ayuda de una espátula, dentro de una cuadrícula de 0.25 m², estableciéndose tres zonas: supra, medio e infralitoral. Los organismos fueron preservados en frascos con formalina al 10% para su posterior análisis. En el laboratorio fueron identificados, contados, y pesados en una balanza de 0.001g de precisión. Se determinó la abundancia total de especies, biomasa, constancia específica y por medio de una revisión bibliográfica se le asignó a cada especie su categoría trófica, clasificándolos en: herbívoros, filtradores, carnívoros y herbívoros -filtradores. Se obtuvo un total de 14 581 individuos (6 397.945 g) representado por 68 especies correspondientes a las clases Gastropoda (39), Bivalvia (23) y Polyplacophora (6); contenidas en nueve órdenes y 31 familias. Los herbívoros fueron el grupo dominante (49%), seguido por filtradores (37%), carnívoros (13 %) y herbívoros-filtradores (1%). Las especies herbívoras y herbívoras-filtradoras dominaron en el área protegida, mientras que en el área expuesta, fueron las carnívoras y filtradoras. Las especies constantes en las seis localidades durante el período de estudio fueron Planaxis nucleus, Mitrella ocellata, M. nycteis, Littorina interrupta, Tegula fasciata, Acmaea leucopleura, Ostrea equestris y Chiton squamosus. La distribución de los moluscos y los diferentes grupos tróficos, pueden estar controlados por adaptaciones morfológicas, así como el nivel de exposición al oleaje y composición del sustrato.</p></abstract>
<kwd-group>
<kwd>mollusc</kwd>
<kwd>rocky littoral</kwd>
<kwd>trophic relations</kwd>
<kwd>Sucre State</kwd>
<kwd>Venezuela</kwd>
<kwd>moluscos</kwd>
<kwd>litoral rocoso</kwd>
<kwd>relaciones tróficas</kwd>
<kwd>Estado de Sucre</kwd>
<kwd>Venezuela</kwd>
</kwd-group>
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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420060006</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-id>S0034-77442006000600018</article-id>
<title-group>
<article-title xml:lang="es">El cangrejo Heterocrypta tommasii (Decapoda: Parthenopidae): adición a la carcinofauna venezolana</article-title>
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<institution>,Universidad de Oriente  </institution>
<addr-line> </addr-line>
<country>Venezuela</country>
</aff>
<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
</pub-date>
<pub-date pub-type="epub">
<year>2006</year>
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<volume>54</volume>
<fpage>131</fpage>
<lpage>134</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600018&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=S0034-77442006000600018&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=S0034-77442006000600018&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The crab Heterocrypta tommasii (Decapoda: Parthenopidae): an addition to the carcinofauna of Venezuela. The crab Heterocrypta tommasii Rodrigues da Costa, 1959 is reported for the first time from Venezuelan marine waters and its main taxonomical features are presented and illustrated. This report extends the range from Colombia, Guyana and Brazil; is the first report of the genus for Venezuela, and increases to six the number of Parthenopidae species known from the country. Rev. Biol. Trop. 54 (Suppl. 3): 131-134. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Se registra por primera vez en aguas marinas venezolanas la presencia del cangrejo Heterocrypta tommasii y se presentan las principales características del espécimen estudiado. Este hallazgo amplía la distribución conocida de la especie (la cual sólo contemplaba Colombia, Guayana y Brasil), establece el primer registro del género Heterocrypta en Venezuela e incrementa a seis el número de especies conocidas de Parthenopidae para este país.</p></abstract>
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<kwd>Caribbean</kwd>
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<kwd>Venezuela</kwd>
<kwd>crustáceos</kwd>
<kwd>biodiversidad</kwd>
<kwd>Caribe</kwd>
<kwd>bentos</kwd>
<kwd>Parthenopoidea</kwd>
<kwd>Venezuela</kwd>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600019&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=S0034-77442006000600019&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=S0034-77442006000600019&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Mollusc communities associated with the green mussel Perna viridis (Mollusca: Bivalvia) and their trophic relations on the north coast of Araya Peninsula, Sucre State, Venezuela. Perna viridis (Linné, 1758) is an Indo-Pacific bivalve of the intertidal zone that has invaded several ecosystems of the north coast of the Sucre State,Venezuela. Bimonthly samplings were carried out between October 1997 and August 1998 to study the mollusc communities associated with this species and their trophic relationships.Studies were conducted on a naturally-occuring bank of mussels two meters deep on the north coast of the peninsula of Araya (10°40’N -48°63’W). Sample organisms were collected withing areas defined by a quadrat of 0.25 m², and were identified to the species level using taxonomic keys that also included bibliographic identification of trophic level. A total of 1 235 individuals of P. viridis were collected, along with 3 163 specimens of associated species belonging to the phylum Mollusca, including bivalves, gastropods and polyplacophora.The associated mollusc organisms represented 50 species corresponding to 10 orders and 24 families, including 25 gastropod species, 22 bivalves and three polyplacophorans. With regard to trophic level 40% of the 50 species were suspensivores, 26% carnivores, 24% herbivores and the residual 10% represented two categories (suspensivore-detritivore, herbivore-suspensivore). Of the suspensivores the most common were: Perna perna, Musculus lateralis, Crassostrea rhizophorae and Ostrea equestris. The carnivore group was dominated by the three species of the Family Columbellidae, Mitrella lunata, Anachis obesa and Nitidella ocellata.The group of herbivores was dominated by two members of the family Fisurellidae, Diodora cayenensis and D. minuta.Two species of suspensivore-detritívore and three species of herbivore-suspensivore were also found in the genus Crepidula. The high percentage of suspensivores was thought indicative, inside this ecosystem, that there is probably a higher degree of nutritious fractions available to this group. Rev. Biol. Trop. 54 (Suppl. 3): 135-144. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Perna viridis es un bivalvo procedente del Indo-Pacífico que habita en la zona intermareal y ha invadido varios ecosistemas de la costa norte del estado Sucre, Venezuela. Con la finalidad de realizar un estudio sobre las comunidades de moluscos asociadas a esta especie y sus relaciones tróficas, se llevaron a cabo muestreos bimensuales entre octubre/97 y agosto/98, en un banco natural de mejillones a dos metros de profundidad en la costa norte de la península de Araya (10°40’N -48°63’W). Los organismos fueron recolectados delimitando el área con una cuadrícula de 0.25 m². Se identificaron los organismos hasta la categoría de especies utilizando claves específicas para moluscos y bibliográficamente se les determinó categoría trófica.Se capturó un total de 1 235 individuos de P. viridis y asociados a la especie 3 163 especímenes pertenecientes al phylum Mollusca, contenidos en tres clases: Bivalvia,Gastropoda y Polyplacophora. Éstas estuvieron representadas por 50 especies correspondientes a 10 órdenes, 24 familias; para los gasterópodos se contabilizaron 25 especies, para los bivalvos 22 y tres para los poliplacóforos. Del total de las especies, 40% fueron filtradoras, 26% carnívoras, 24% herbívoras y el 10% restante presentó dos categorías.De las filtradoras las más representativas fueron: Perna perna, Musculus lateralis, Crassostrea rhizophorae y Ostrea equestris; en el grupo de los carnívoros dominaron tres especies de la familia Columbellidae:Mitrella lunata, Anachis obesa y Nitidella ocellata y para el grupo de los herbívoros destacaron dos especies de la familia Fisurellidae: Diodora cayenensis y D. minuta. Se registraron dos especies filtradoras-detritívoras, y tres especies herbívoras-filtradoras representantes del género C repidula. El alto porcentaje de filtradores sería un indicativo de que dentro de este sistema probablemente hay una mayor disponibilidad de fracciones alimenticias para este grupo.</p></abstract>
<kwd-group>
<kwd>molluscs</kwd>
<kwd>green mussels</kwd>
<kwd>Perna viridis</kwd>
<kwd>trophic relationships</kwd>
<kwd>ecology</kwd>
<kwd>moluscos</kwd>
<kwd>mejillón verde</kwd>
<kwd>Perna viridis</kwd>
<kwd>relaciones tróficas</kwd>
<kwd>ecología</kwd>
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<aff id="A01">
<institution>,University of Miami  </institution>
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<country>USA</country>
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<aff id="A02">
<institution>,Southeast Fisheries Science Center  </institution>
<addr-line>Miami Florida</addr-line>
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<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600020&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=S0034-77442006000600020&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=S0034-77442006000600020&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Sexual recruitment of the staghorn coral, Acropora cervicornis, is accepted to be very rare. Instead, these branching corals proliferate through fragmentation leading to dense mono-specific and possibly monoclonal stands. For acroporid corals, which have suffered drastic population declines, dominance of asexual reproduction results in low levels of genotypic diversity and limited ability to re-colonize extirpated areas. Small colonies with a single encrusting, symmetrical base, and few incipient branches are frequently presumed to be the result of a settled planula (i.e. sexual reproduction). Here, we show that colonies fitting this description (i.e., presumed sexual recruits) can result from asexual fragmentation. Acropora cervicornis colonies (~20 cm diameter) were tagged and observed over eighteen months. In several cases, colony offshoots fused with the adjacent substrate forming secondary disc-like attachment points. Following natural fragmentation, these discs of tissue became separated from the original colony, and were observed to heal and give rise to smaller colonies with striking similarity to the expected morphology of a sexual recruit. Thus, presuming a colony is a sexual recruit based on appearance is unreliable and may lead to inflated expectations of genetic diversity among populations. The accurate assessment of recruitment and genetic diversity is crucial to predicting the recovery potential of these imperiled and ecologically irreplaceable reef corals. Rev. Biol. Trop. 54 (Suppl. 3): 145-151. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Se ha aceptado que el reclutamiento sexual del coral asta de venado, Acropora cervicornis, es muy raro. Por el contrario, estos corales ramificados proliferan a través de fragmentación, generando densas bases monoespecíficas e incluso monoclonales. Para corales acropóridos, los cuales han sufrido disminuciones de población drásticas, la dominancia de reproducción asexual resulta en bajos niveles de diversidad genotípica y abilidad limitada para recolonizar áreas de donde han sido erradicados. Frecuentemente se presume que las colonias pequeñas con una sola base incrustante simétrica y unas pocas ramas incipientes, son el resultado del asentamiento de una plánula (reproducción sexual). Aquí, nosotros demostramos que algunas colonias que calzan con esta descripción (supuesta reproducción sexual) pueden resultar de fragmentación asexual. Se etiquetaron y observaron colonias de Acropora cervicornis (~20 cm de diámetro) durante 18 meses. En muchos casos, los retoños de la colonia se fusionaron con el sustrato adyacente formando puntos de acoplamiento con forma de disco. Siguiendo con la fragmentación natural, estos discos de tejido se separaron de la colonia original, cicatrizaron y dieron paso a pequeñas colonias con tremenda similitud a la morfología esperada para un recluta sexual. Por lo tanto, asumir que una colonia es un recluta de origen sexual basándose en apariencia es poco fiable y puede generar expectativas infladas de diversidad genética entre poblaciones. La evaluación certera del reclutamiento y la diversidad genética es crucial para predecir la recuperación potencial de estos arrecifes de coral, los cuales están en peligro y son irremplazables.</p></abstract>
<kwd-group>
<kwd>recruitment</kwd>
<kwd>fragmentation</kwd>
<kwd>staghorn coral</kwd>
<kwd>clonal</kwd>
<kwd>colony</kwd>
<kwd>Acropora cervicornis</kwd>
<kwd>reclutamiento</kwd>
<kwd>fragmentación</kwd>
<kwd>coral asta de venado</kwd>
<kwd>clonal</kwd>
<kwd>colonia</kwd>
<kwd>Acropora cervicornis</kwd>
</kwd-group>
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<article-id>S0034-77442006000600021</article-id>
<title-group>
<article-title xml:lang="en">Status of aspergillosis and sea fan populations in Curaçao ten years after the 1995 Caribbean epizootic</article-title>
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<institution>,University of North Carolina Wilmington  </institution>
<addr-line> North Carolina</addr-line>
<country>USA</country>
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<institution>,Radboud University Nijmegen  </institution>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600021&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=S0034-77442006000600021&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=S0034-77442006000600021&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>In 1995, a survey of sea fan corals was conducted in Curaçao during a Caribbean-wide outbreak of the sea fan disease aspergillosis. The survey was repeated in 2005 using the same methodology and identical sites to examine changes in sea fan populations 10 years after the initial epizootic. Necrotic lesions typical of aspergillosis were present on as many sea fans in 2005 as in 1995 (mean ± SE: 52 ± 6 vs 43 ± 10%). The disease also showed no significant variation in virulence (9.6 ± 1.2 vs 8.8 ± 1.0% tissue loss per diseased colony). However, the average number of sea fan colonies per 10 m² decreased from 2.7 ± 1.1 to 0.7 ± 0.2 over the 10-year period, a decline of almost 75%. This decrease occurred for all colony sizes, but was more pronounced among small colonies, resulting in an overall trend of domination by large colonies. These results support that aspergillosis can have a significant, long-term impact on sea fan population size and structure. The continued presence of the disease in 2005 could be contributing to reduced recruitment and/or selective mortality among the smallest colonies. This study provides no indication that host resistance against aspergillosis could reverse the decline of Caribbean sea fan corals. Rev. Biol. Trop. 54 (Suppl. 3): 153-160. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>En 1995, se realizó un sondeo de los abanicos de mar durante un brote de aspergilosis, una enfermedad de abanicos de mar extendida en todo el Caribe. En el año 2005 se repitió el sondeo utilizando exactamente la misma metodología y los mismos sitios para examinar cambios en las poblaciones tras 10 años del inicio del brote. Se presentaron lesiones necróticas típicas de la aspergilosis en tantos abanicos en el 2005, como en 1995 (promedio ± ES: 52 ± 6 vs 43 ± 10%). La enfermedad tampoco mostró variaciones significativas en la virulencia (9.6 ± 1.2 vs 8.8 ± 1.0%, pérdida de tejido por colonia enferma). Sin embargo, el número promedio de colonias de abanico de mar por cada 10 m² bajó desde 2.7 ± 1 hasta 0.7 ± 0.2 en este período de 10 años, una disminución de casi 75%. Este decrecimiento ocurrió en colonias de todo tamaño, pero fue más pronunciado en colonias pequeñas, produciendo una tendencia general de dominancia de colonias grandes. Estos resultados apoyan la idea de que la aspergilosis puede tener un impacto significativo a largo plazo en el tamaño y estructura poblacional de los abanicos de mar. La continuidad en la presencia de la enfermedad en el 2005 puede estar contribuyendo a la reducción en el reclutamiento y/o a la mortalidad selectiva de las colonias más pequeñas. Este estudio no provee ninguna evidencia de que la resistencia del hospedero contra la aspergilosis pueda revertir el decrecimiento de los abanicos de mar en el Caribe.</p></abstract>
<kwd-group>
<kwd>Aspergillosis</kwd>
<kwd>Caribbean</kwd>
<kwd>coral disease</kwd>
<kwd>coral reefs</kwd>
<kwd>gorgonians</kwd>
<kwd>sea fan</kwd>
<kwd>population structure</kwd>
<kwd>aspergilosis</kwd>
<kwd>Caribe</kwd>
<kwd>enfermedad de coral</kwd>
<kwd>arrecife de coral</kwd>
<kwd>gorgonáceos</kwd>
<kwd>abanico de mar</kwd>
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<institution>,University of Puerto Rico  </institution>
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<institution>,University of Puerto Rico  </institution>
<addr-line>Mayagüez </addr-line>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600022&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=S0034-77442006000600022&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=S0034-77442006000600022&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Three anomalies are described: a scythebill in Greater Antillean Grackle, Quiscalus niger (Boddaert) (Passeriformes: Emberizidae), a crown color pattern in Rock Beauty, Holacanthus tricolor (Bloch) (Perciformes: Pomacanthidae), and a double-spot color pattern in Butter Hamlet, Hypoplectrus unicolor (Walbaum) (Perciformes: Pomacanthidae). Bill anomalies are generally thought to be genetic in origin and genetic changes in bill shape can occur rapidly in a population. The scythebill anomally demonstrates how quickly a drastic bill modification may occur. The crown color pattern anomaly is similar to distinctive markings found in other members of this genus [Queen Angelfish, H. ciliaris (Linnaeus) and hybrid Townsend Angelfish H. ciliaris X H. bermudensis Goode] in the tropical western Atlantic. It suggests how quickly this pattern could have originated in the other species, and/or some propensity of this pattern in the genus. The distinct double-spot color pattern anomaly suggests how quickly new color patterns can originate in genus Hypoplectrus. This is important because species in this genus are distinguished almost solely on the basis of color pattern and speciation may be occurring rapidly. Anomalies should be recorded because they may give us some hints at the genetic origin of species characters and some could represent potentially inheritable characters. We suggest these potentially inheritable characters could be recognized and described when they first arise in an individual and before they become inherited by a population. Following these potentially inheritable characters could help to explain how such characters enter into a population. This approach to the study of inherited characters could fill a void in our knowledge of evolution and speciation. Rev. Biol. Trop. 54 (Suppl. 3): 161-169. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Se describen tres anomalías: el pico de guadaña en el chinchilín, Quiscalus niger (Boddaert) (Passeriformes: Emberizidae), un patrón de color de corona en el isabelita medioluto, Holacanthus tricolor (Bloch) (Perciformes: Pomacanthidae), y un patrón de color de doble mancha en el vaca blanca, Hypoplectrus unicolor (Walbaum) (Perciformes: Pomacanthidae). Generalmente se piensa que las anomalías en el pico son de origen genético y que los cambios genéticos en la forma del pico pueden ocurrir rápidamente en una población. La anomalía del pico de guadaña demuestra cuan rápido puede ocurrir una modificación drástica del pico. La anomalía del patrón de color de corona es similar a otras marcas distintivas encontradas en otros miembros de este género [isabelita reina, H. ciliaris (Linnaeus) y el híbrido isabelita azul H. ciliaris X H. bermudensis Goode] en el Atlántico occidental tropical y también indica cambios rápidos. Esto es importante porque las especies de este género se distinguen casi solamente por patrones de color. Las anomalías deberían ser registradas ya que podrían darnos algunas pistas acerca del origen genético de las características de las especies. Proponemos que los caracteres potencialmente heredables pueden reconocerse y describirse cuando aparecen en un individuo, antes de que sean heredados a la población, llenando un vacío en nuestro conocimiento de la evolución y la especiación.</p></abstract>
<kwd-group>
<kwd>anomalies</kwd>
<kwd>crown color pattern</kwd>
<kwd>scythebill</kwd>
<kwd>double-spot color pattern</kwd>
<kwd>Rock Beauty</kwd>
<kwd>Greater Antillean Grackle</kwd>
<kwd>Butter Hamlet</kwd>
<kwd>Caribbean</kwd>
<kwd>anomalías</kwd>
<kwd>patrón de color de corona</kwd>
<kwd>pico de guadaña</kwd>
<kwd>patrón de color de doble mancha</kwd>
<kwd>isabelita medioluto</kwd>
<kwd>chinchilín (mozambique, chango)</kwd>
<kwd>vaca blanca</kwd>
<kwd>Caribe</kwd>
</kwd-group>
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<front>
<journal-meta>
<journal-id pub-id-type="pid">S0034-774420060006</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>S0034-77442006000600023</article-id>
<title-group>
<article-title xml:lang="en">New geographic records of Hamlets, Hypoplectrus spp. (Serranidae), in the Caribbean Sea</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author">
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<surname>Williams, Jr</surname>
<given-names>Ernest H</given-names>
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<xref ref-type="aff" rid="A01"/>
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<given-names>Lucy</given-names>
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<given-names>Caroline S</given-names>
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<given-names>Robert</given-names>
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<aff id="A01">
<institution>,University of Puerto Rico  </institution>
<addr-line>Mayagüez </addr-line>
<country>Puerto Rico</country>
</aff>
<aff id="A02">
<institution>,University of Puerto Rico  </institution>
<addr-line>Mayagüez </addr-line>
<country>Puerto Rico</country>
</aff>
<aff id="A03">
<institution>,Florida Caribbean Science Center  </institution>
<addr-line> </addr-line>
</aff>
<aff id="A04">
<institution>,Web Web Media  </institution>
<addr-line>San Diego California</addr-line>
<country>USA</country>
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<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
</pub-date>
<pub-date pub-type="epub">
<year>2006</year>
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<volume>54</volume>
<fpage>171</fpage>
<lpage>173</lpage>
<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600023&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=S0034-77442006000600023&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=S0034-77442006000600023&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The exact number of species of hamlets, Hypoplectrus spp., in the Caribbean is controversial and the geographic distributions of these species/forms are poorly documented. We report Curaçao, Netherlands Antilles, as a new locality for the Barred Hamlet, H. puella (Cuvier), and Shy Hamlet, H. guttavarius (Poey); and St. John and St. Thomas, U.S. Virgin Islands, for the Tan Hamlet, Hypoplectrus sp. The Black Hamlet, H. nigricans (Poey), has previously been reported from Curaçao, but we did not see it there. Rev. Biol. Trop. 54 (Suppl. 3): 171-173. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>En el Caribe, el número exacto de especies de pez vaca, Hypoplectrus spp., es controversial y la distribución geográfica de estas especies/variedades está pobremente documentada. Presentamos Curaçao, Antillas Holandesas, como nueva localidad para el pez vaca de barras, H. puella (Cuvier) y el vaca bicolor, H. guttavarius (Poey). Agregamos St. John y St. Thomas, Islas Vírgenes de los EUA, al ámbito del &quot;Tan Hamlet&quot;, Hypoplectrus sp. Anteriormente se dijo que en Curaçao se halla el pez vaca negra, H. nigricans (Poey), pero no lo vimos en nuestros muestreos.</p></abstract>
<kwd-group>
<kwd>Hamlets</kwd>
<kwd>geographic distribution</kwd>
<kwd>Curaçao</kwd>
<kwd>U.S. Virgin Islands</kwd>
<kwd>Hypoplectrus spp</kwd>
<kwd>pez vaca</kwd>
<kwd>distribución geográfica</kwd>
<kwd>Curaçao</kwd>
<kwd>Islas Vírgenes</kwd>
<kwd>Hypoplectrus spp</kwd>
</kwd-group>
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<journal-id pub-id-type="pid">S0034-774420060006</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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<article-title xml:lang="en">Isopods (Isopoda: Aegidae, Cymothoidae, Gnathiidae) associated with Venezuelan marine fishes (Elasmobranchii, Actinopterygii)</article-title>
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<given-names>Lucy</given-names>
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<given-names>Ernest H</given-names>
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<aff id="A01">
<institution>,University of Puerto Rico  </institution>
<addr-line>Mayagüez </addr-line>
<country>USA</country>
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<aff id="A02">
<institution>,University of Puerto Rico  </institution>
<addr-line> </addr-line>
<country>USA</country>
</aff>
<aff id="A03">
<institution>,Universidad de Oriente  </institution>
<addr-line>Cumaná </addr-line>
<country>Venezuela</country>
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<pub-date pub-type="pub">
<month>12</month>
<year>2006</year>
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<pub-date pub-type="epub">
<year>2006</year>
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<fpage>175</fpage>
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<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600024&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=S0034-77442006000600024&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=S0034-77442006000600024&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>The parasitic isopod fauna of fishes in the southern Caribbean is poorly known. In examinations of 12 639 specimens of 187 species of Venezuelan fishes, the authors found 10 species in three families of isopods (Gnathiids, Gnathia spp. from Diplectrum radiale *, Heteropriacanthus cruentatus *, Orthopristis ruber * and Trachinotus carolinus *; two aegids, Rocinela signata from Dasyatis guttata *, H. cruentatus *, Haemulon aurolineatum *, H. steindachneri * and O. ruber ; and Rocinela sp. from Epinephelus flavolimbatus *; five cymothoids: Anilocra haemuli from Haemulon boschmae *, H. flavolineatum * and H. steindachneri *; Anilocra cf haemuli from Heteropriacanthus cruentatus *; Haemulon bonariense*, O. ruber*, Cymothoa excisa in H. cruentatus *; Cymothoa oestrum in Chloroscombrus chrysurus, H. cruentatus* and Priacanthus arenatus ; Cymothoa sp. in O. ruber; Livoneca sp. from H. cruentatus *; and Nerocila fluviatilis from H. cruentatus * and P. arenatus *). The Rocinela sp. and A. cf haemuli in the southern Caribbean could represent new species. The abundance of A. cf haemuli appears to have drastically reduced from 1994 to 1999 in the Gulf of Cariaco. The Cymothoa sp. represents an undescribed species that is apparently host specific to O. ruber . It does not occur in the Gulf of Cariaco, but is relatively abundant on the Caribbean coast of Sucre State, Venezuela. The Livoneca sp. is an undescribed species host specific to Diapterus rhombeus, Cymothoa excisa and C. oestrum were thought to have distinct host preferences, but both infected the Heteropriacanthus cruentatus in the present study.Gnathia spp. are reported from Venezuelan waters for the first time. Twenty new host records* are noted. The fish-associated isopod fauna is much more extensive and important than has previously been suspected. Rev. Biol. Trop. 54 (Suppl. 3): 175-188. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Se conoce muy poco acerca de la fauna de isópodos parásitos de peces en el Caribe Sur. Tras examinar 12 639 especímenes de 187 especies de peces de Venezuela, los autores encontraron 10 especies de isópodos distribuidos en tres familias. Los asteriscos indican nuevos registros (Gnátidos, Gnathia spp. en Diplectrum radiale*, Heteropriacanthus cruentatus*; Orthopristis ruber* y Trachinotus carolinus*; dos aégidos, Rocinela signata en Dasyatis guttata*, H. cruentatus*, Haemulon aurolineatum*, H. steindachneri * y O. ruber ; y Rocinela sp. en Epinephelus flavolimbatus*; cinco cimotoidos: Anilocra haemuli en Haemulon boschmae*, H. flavolineatum* y H.steindachneri*; Anilocra cf haemuli en Heteropriacanthus cruentatus*; Haemulon bonariense*, O. ruber*; Cymothoa excise in H. cruentatus*; Cymothoa oestrum en Chloroscombrus chrysurus, H. cruentatus* y Priacanthus arenatus; Cymothoa sp. en O. ruber; Livoneca sp. en H. cruentatus*; y Nerocila fluviatilis en H. cruentatus* y P. arenatus*). Las especies Rocinela sp.y A.cf haemuli en el Caribe sur podrían representar especies distintas. La abundancia de A. cf haemuli en el Golfo de Coriaco parece haberse reducido drásticamente entre 1994 a 1999. Cymothoa sp.es una especie no descrita que aparentemente parasita específicamente a O. ruber. No se le encuentra en el Golfo de Cariaco, pero es relativamente abundante en la costa Caribe del Estado de Sucre, Venezuela. Livoneca sp. (especie sin describir) parasita específicamente a Diapterus rhombeus. Anteriormente se pensaba que Cymothoa excisa y C. oestrum tenían distintas preferencias de hospedero, pero ambas infectan a Heteropriacanthus cruentatus. Gnathia spp. Son además primer registro en aguas venezolanas. Se informan en total 20 nuevos registros. La fauna de isópodos asociados a peces es mucho más extensa e importante de lo que se sospechaba.</p></abstract>
<kwd-group>
<kwd>fish-parasitic isopods</kwd>
<kwd>Venezuela</kwd>
<kwd>new species</kwd>
<kwd>new host</kwd>
<kwd>new locality records</kwd>
<kwd>isópodos parásitos de peces</kwd>
<kwd>Venezuela</kwd>
<kwd>nuevas especies</kwd>
<kwd>nuevos hospederos</kwd>
<kwd>nuevos registros de localidad</kwd>
</kwd-group>
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<article-meta>
<article-id>S0034-77442006000600025</article-id>
<title-group>
<article-title xml:lang="es">Actividades biológicas del extracto acuoso de la esponja Aplysina lacunosa (Porifera: Aplysinidae)</article-title>
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<aff id="A01">
<institution>,Universidad de Oriente  </institution>
<addr-line>Cumaná </addr-line>
<country>Venezuela</country>
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<copyright-statement/>
<copyright-year/>
<self-uri xlink:href="http:/www.scielo.sa.cr/scielo.php?script=sci_arttext&amp;pid=S0034-77442006000600025&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=S0034-77442006000600025&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=S0034-77442006000600025&amp;lng=en&amp;nrm=iso"></self-uri><abstract abstract-type="short" xml:lang="en"><p>Biological activity of an aqueons extract of the sponge Aplysina lacunosa (Porifera: Aplysinidae). The aqueous extract and protein precipitate of Aplysina lacunosa (Pallas, 1776) were studied to assess their hemagglutinating, hemolysing, antibacterial, and antifungal activities. Specimens of the marine sponge were collected in El Morro de Tigüitigüe, Santa Fe, Sucre state, Venezuela. The active protein was separated by molecular exclusion chromatography and its molar mass estimated by SDS-PAGE electrophoresis. The sponge A. lacunosa has a protein with a molar mass of about 43 000 Daltons which is capable of agglutinating human erythrocytes of the blood groups A, B, and O in a strong and unspecific mode. The assayed samples did not evidence any hemolysing activity. As for the antibacterial assay, only the aqueous extract was able to inhibit the growth of Enterococcus faecalis, Bacillus cereus, Escherichia coli, and Salmonella enteritidis, with inhibition halos of 24, 20, 24, and 22 mm, respectively. None of the samples exhibited antifungal activity. The chemical analysis of the aqueous extract revealed the presence of several secondary metabolites. It is presumed that its hemagglutinating activity is mediated by agglutinative proteins. The antibacterial activity could be attributed to the presence of saponins, alkaloids, tannins, and polyphenols, which are highly antimicrobial compounds. Poriferans are a rich source of bioactive compounds that can be used in the development of new drugs potentially useful in medicine. Rev. Biol. Trop. 54 (Suppl. 3): 189-200. Epub 2007 Jan. 15.</p></abstract>
<abstract abstract-type="short" xml:lang="es"><p>Evaluamos el extracto acuoso y precipitado de proteínas de Aplysina lacunosa, en relación con su actividad hemaglutinante, hemolizante, antibacteriana y antimicótica. Los ejemplares de la esponja marina fueron recolectados en el Morro de Tigüitigüe, Santa Fe, Estado Sucre, Venezuela. La proteína activa fue separada por cromatografía de exclusión molecular; y su masa molar fue estimada por electroforesis SDS-PAGE. La esponja A. lacunosa posee una proteína con masa molar aproximada de 4.000 Daltons capaz de aglutinar fuertemente y de manera inespecífica los eritrocitos humanos de los grupos sanguíneos A, B y O. No se observó actividad hemolizante por parte de las muestras ensayadas. Únicamente el extracto acuoso fue capaz de inhibir el crecimiento de Enterococcus faecalis, Bacillus cereus, Escherichia coli y Salmonella enteritidis con halos de inhibición de 24, 20, 24, 22 mm, respectivamente; ninguna de las muestras exhibió actividad antifúngica. El análisis químico del extracto acuoso reveló la presencia de diversos metabolitos secundarios. Se presume que la actividad hemaglutinante se deba a la presencia de proteínas aglutinantes. La actividad antibacteriana podría atribuirse a la presencia de saponinas, alcaloides, taninos y polifenoles, compuestos altamente antimicrobianos. Los poríferos constituyen una fuente rica de compuestos bioactivos que pueden ser utilizados para el desarrollo de nuevos fármacos.</p></abstract>
<kwd-group>
<kwd>Marine sponge</kwd>
<kwd>Aplysina lacunosa</kwd>
<kwd>agglutinins</kwd>
<kwd>secondary metabolites</kwd>
<kwd>antibacterial activity</kwd>
<kwd>aqueous extract</kwd>
<kwd>esponja marina</kwd>
<kwd>Aplysina lacunosa</kwd>
<kwd>aglutininas</kwd>
<kwd>metabolitos secundarios</kwd>
<kwd>actividad antibacterial</kwd>
<kwd>extracto acuoso</kwd>
</kwd-group>
</article-meta>
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