Its length polymorphism in oysters and its use in species identification

In an effort to develop genetic markers for oyster identification, we studied length polymorphism in internal transcribed spacers (ITS) between major ribosomal RNA genes in 12 common species of Ostreidae: Crassostrea virginica, C. rhizophorae, C. gigas, C. angulata, C. sikamea, C. ariakensis, C. hongkongensis, Saccostrea echinata, S. glomerata, Ostrea angasi, O. edulis, and O. conchaphila. We designed two pairs of primers and optimized PCR conditions for simultaneous amplification of ITS 1 and ITS2 in a single PCR. Amplification was successful in all 12 species, and PCR products were visualized on high-resolution agarose gels. ITS2 was longer than ITS 1 in all Crassostrea and Saccostrea species, whereas they were about the same size in the three Ostrea species. No intraspecific variation in ITS length was detected. Among species, the length of ITS I and ITS2 was polymorphic and provided unique identification of 8 species or species pairs: C. ariakensis, C. hongkongensis, C. sikamea, O. conchaphila, C. virginica/C. rhizophorae, C. gigas/C. angulata, S. echinata/S. glonzerata, and O. angasi/O. edulis. The ITS assay provides simple, rapid and effective identification of C. ariakensis and several other oyster species. Because the primer sequences are conserved, the ITS assay may be useful in the identification of other bivalve species.

Resumos...

Análise proteômica de raízes de feijão (Phaseolus vulgaris) inoculadas com Rhizobium tropici. Teste para comprovar a eficiência do método de extração e determinação de ácido fítico em sementes de soja utilizado na Embrapa Soja. Auditoria de comunicação: avaliando os veículos de comunicação interna da Embrapa Soja. Utilização da técnica de espectrofotometria do infravermelho próximo (NIR) para análise discriminante dos ácidos graxos oléico e linoléico de genótipos de girassol. Análise da disponibilidade hídrica para a cultura da soja nas safras 2004/05 e 2009/10 em Londrina, PR . Calibração de psicrômetros para avaliações de potencial hídrico foliar. Avaliação de ácidos graxos da soja: grão inteiro, casca, cotilédones e hipocótilo. Variabilidade temporal da produtividade da soja após conversão do preparo convencional para o sistema plantio direto. COMUT na biblioteca da Embrapa Soja. EM DIA: Boletim interno compartilhando informações. Sistema Web para estimativas de perdas por seca na cultura da soja. Portais Web desenvolvidos no laboratório de Bioinformática da Embrapa Soja. Validação de um método para detecção e quantificação de soja cultivance® tolerante a herbicidas imidazolinonas por PCR . Índice de vegetação por diferença normalizada (NDVI) de cultivares de soja sob três níveis de disponibilidade hídrica no solo. Avaliação do fluxo de seiva em cultivares de soja em três níveis de disponibilidade hídrica no solo. A importância do controle de qualidade dos inoculantes. Comportamento exploratório de ninfas recém eclodidas de Edessa meditabunda (F.) (Heteroptera: Pentatomidae) sobre a superfície dos córions. Produção de brotos de soja da cultivar BRS 216. Teste de aceitabilidade de brotos de soja da cultivar BRS 216. Análise de lignina com diferentes massas de tegumento de soja utilizando método gravimétrico. Desenvolvimento e caracterização físico-química de biscoitos com farinha de soja orgânica de cultivares especiais para a alimentação humana. Análise sensorial de biscoitos com farinha de soja orgânica de cultivares especiais para a alimentação humana. Avaliação de genótipos de soja de diferentes grupos de maturação e resistência aos percevejos. Métodos químicos para extração de boro no solo. Abordagem computacional para a identificação de elementos cis-regulatórios no genoma da soja. Quebra de dormência em sementes de girassol silvestre utilizando ácido giberélico. Teor relativo de água em cultivares de soja sob três níveis de disponibilidade hídrica no solo. Soybean gene express: plataforma para análise de expressão diferencial em bibliotecas subtrativas de CDNA. Biologia e exigências térmicas do ácaro vermelho Tetranychus gigas. Características biológicas de Telenomus remus em diferentes hospedeiros após serem criados em de ovos de Anticarsia gemmatalis e Spodoptera frugiperda por uma geração. Enfoque sobre o plano de saúde dos empregados da Embrapa no contexto do pacote de benefícios sociais oferecidos pela empresa. Dinâmica populacional do ácaro verde Mononychellus planki em cultivares de soja. Envelhecimento, trabalho e tempo livre: elaborando projetos de vida. Teor de isoflavonas em vinte cultivares de soja semeadas em Londrina e Ponta Grossa. Utilização de Pseudomonas fluorescens no controle biológico de Macrophomina phaseolina. Algoritmo computacional para determinar o perfil mínimo de marcadores moleculares que discriminam um conjunto de cultivares. Qualidade física do solo em um sistema de integração lavoura-pecuária com diferentes pressões de pastejo. Diversidade de estirpes do gênero Burkholderia em solos do cerrado brasileiro baseado no sequenciamento do gene ribossomal 16S. Estudo da diversidade genética de isolados de Corynespora cassiicola (Berk. & M.A. Curtis) C.T. Wei.

Ecotoxicology of marine biotoxins in bivalve shellfish

A small proportion of harmful algae produce toxins which are harmful to human health. Strict monitoring programmes are in place within Ireland and the EU to effectively manage risk to human consumers of shellfish species that have accumulated marine biotoxins in their tissues. However, little is known about the impacts of HABs on shellfish health. This study used Solid Phase Adsorption and Toxin Tracking (SPATT) for the passive sampling of algal biotoxins at Lough Hyne Marine Nature Reserve in West Cork, Ireland. Spatial and temporal monitoring of the incidence of a wide range of lipophilic toxins was assessed over a 4-month period. Active sampling accumulated sufficient quantities of toxin for use in subsequent experimentation. In addition to commonly occurring Diarrhetic Shellfish Poisoning (DSP) toxins, Dinophysis toxin-1 and Pinnatoxin-G were both detected in the samples. This is the first identification of these latter two toxins in Irish waters. The effects of the DSP toxin okadaic acid (OA) were investigated on three shellfish species: Mytilus edulis, Ruditapes philippinarum and Crassostrea gigas. Histological examination of the gill, mantle and hepatopancreas tissues revealed varying intensity of damage depending both on the tissue type and the species involved. At the cellular level, flow cytometric analysis of the differential cell population distribution was assessed. No change in cell population distribution was observed in Mytilus edulis or Ruditapes philippinarum, however significant changes were observed in Crassostrea gigas granulocytes at the lower levels of toxin exposure. This indicated a chemically-induced response to OA. DNA fragmentation was measured in the haemolymph and hepatopancreas cells post OA-exposure in Mytilus edulis and Crassostrea gigas. A significant increase in DNA fragmentation was observed in both species over time, even at the lowest OA concentrations. DNA fragmentation could be due to genotoxicity of OA and/or to the induction of cell apoptosis.

Assessing the sensitivity of blue mussel beds to pressures associated with human activities.

The Joint Nature Conservation Committee (JNCC) commissioned this project to generate an improved understanding of the sensitivities of blue mussel (Mytilus edulis) beds, found in UK waters, to pressures associated with human activities in the marine environment. The work will provide an evidence base that will facilitate and support management advice for Marine Protected Areas, development of UK marine monitoring and assessment, and conservation advice to offshore marine industries. Blue mussel beds are identified as a Habitat of Principle Importance (HPI) under the Natural Environment and Rural Communities (NERC) Act 2006, as a Priority Marine Feature (PMF) under the Marine (Scotland) Act 2010, and included on the OSPAR (Annex V) list of threatened and declining species and habitats. The purpose of this project was to produce sensitivity assessments for the blue mussel biotopes included within the HPI, PMF and OSPAR habitat definitions, and clearly document the supporting evidence behind the assessments and any differences between them. A total of 20 pressures falling in five categories - biological, hydrological, physical damage, physical loss, and pollution and other chemical changes - were assessed in this report. The review examined seven blue mussel bed biotopes found on littoral sediment and sublittoral rock and sediment. The assessments were based on the sensitivity of M. edulis rather than associated species, as M. edulis was considered the most important characteristic species in blue mussel beds. To develop each sensitivity assessment, the resistance and resilience of the key elements are assessed against the pressure benchmark using the available evidence gathered in this review. The benchmarks were designed to provide a ‘standard’ level of pressure against which to assess sensitivity. Blue mussel beds were highly sensitive to a few human activities: • introduction or spread of non-indigenous species (NIS); • habitat structure changes - removal of substratum (extraction); and • physical loss (to land or freshwater habitat). Physical loss of habitat and removal of substratum are particularly damaging pressures, while the sensitivity of blue mussel beds to non-indigenous species depended on the species assessed. Crepidula fornicata and Crassostrea gigas both had the potential to outcompete and replace mussel beds, so resulted in a high sensitivity assessment. Mytilus spp. populations are considered to have a strong ability to recover from environmental disturbance. A good annual recruitment may allow a bed to recovery rapidly, though this cannot always be expected due to the sporadic nature of M. edulis recruitment. Therefore, blue mussel beds were considered to have a 'Medium' resilience (recovery within 2-10 years). As a result, even where the removal or loss of proportion of a mussel bed was expected due to a pressure, a sensitivity of 'Medium' was reported. Hence, most of the sensitivities reported were 'Medium'. It was noted, however, that the recovery rates of blue mussel beds were reported to be anywhere between two years to several decades. In addition, M. edulis is considered very tolerant of a range of physical and chemical conditions. As a result, blue mussel beds were considered to be 'Not sensitive' to changes in temperature, salinity, de-oxygenation, nutrient and organic enrichment, and substratum type, at the benchmark level of pressure. The report found that no distinct differences in overall sensitivity exist between the HPI, PMF and OSPAR definitions. Individual biotopes do however have different sensitivities to pressures, and the OSPAR definition only includes blue mussel beds on sediment. These differences were determined by the position of the habitat on the shore and the sediment type. For example, the infralittoral rock biotope (A3.361) was unlikely to be exposed to pressures that affect sediments. However in the case of increased water flow, mixed sediment biotopes were considered more stable and ‘Not sensitive’ (at the benchmark level) while the remaining biotopes were likely to be affected.

Using a clearly documented, evidence-based approach to create sensitivity assessments allows the assessment basis and any subsequent decision making or management plans to be readily communicated, transparent and justifiable. The assessments can be replicated and updated where new evidence becomes available ensuring the longevity of the sensitivity assessment tool. For every pressure where sensitivity was previously assessed as a range of scores in MB0102, the assessments made by the evidence review have supported one of the MB0102 assessments. The evidence review has reduced the uncertainty around assessments previously undertaken in the MB0102 project (Tillin et al., 2010) by assigning a single sensitivity score to the pressures as opposed to a range. Finally, as blue mussel bed habitats also contribute to ecosystem function and the delivery of ecosystem services, understanding the sensitivity of these biotopes may also support assessment and management in regard to these. Whatever objective measures are applied to data to assess sensitivity, the final sensitivity assessment is indicative. The evidence, the benchmarks, the confidence in the assessments and the limitations of the process, require a sense-check by experienced marine ecologists before the outcome is used in management decisions.

Impacts of climate change on non-native species

Anthropogenic changes to climate and extreme weather events have already led to the introduction of non-native species (NNS) to the North Atlantic. Regional climate models predict that there will be a continuation of the current trend of warming throughout the 21st century providing enhanced opportunities for NNS at each stage of the invasion process. Increasing evidence is now available to show that climate change has led to the northwards range expansion of a number of NNS in the UK and Ireland, such as the Asian club tunicate Styela clava and the Pacific oyster Crassostrea gigas. Providing definitive evidence though of the direct linkage between climate change and the spread of the majority of NNS is extremely challenging, due to other confounding factors, such as anthropogenic activity. Localised patterns of water movement and food supply may also be complicating the overall pattern of northwards range expansion, by preventing the expansion of some NNS, such as the slipper limpet Crepidula fornicata and the Chilean oyster Ostrea chilensis, from a particular region. A greater understanding of the other aspects of climate change and increased atmospheric CO2, such as increased rainfall, heat waves, frequency of storm events, and ocean acidification may aid in increasing the confidence that scientists have in predicting the long term influence of climate change on the introduction, spread and establishment of NNS.

Polyopes lancifolius (Halymeniales, Rhodophyta), a new component of the Japanese marine flora introduced to Europe

Polyopes lancifolius (Harvey) S. Kawaguchi & H.W. Wang has been recorded for the first time in Europe, during the summer or 2008. A small population was discovered in the Gulf of Morbihan (northeast Atlantic, France). This is the first observation of P. lancifolius outside its native range. Vegetative and reproductive morphological features are compared with previous descriptions. rbcL sequences show no divergence from Japanese populations. Imports of Pacific oysters Crassostrea gigas (Thunberg 1793) are likely to be responsible for its accidental introduction into the Gulf of Morbihan, either directly from northwest Pacific regions or indirectly (secondary dispersal) by transfers from another European oyster farming site. The history of previous algal introductions from Japan suggests that if it becomes successfully established at Morbihan, the species is likely to spread to other European coastal areas.

Phylogeographical analyses of shellfish viruses: inferring a geographical origin for ostreid herpesviruses OsHV-1 (Malacoherpesviridae)

Mortality episodes have regularly been affecting the shellfish industry throughout its history. Some of these mortalities, especially in the oyster industry, have been attributed to herpesviruses. Purification of viral particles and molecular characterization have led to the development of routine monitoring, as well as improved taxonomic classification. Ostreid herpesviruses (Malacoherpesviridae), mostly affecting Pacific oysters Crassostrea gigas, have been sporadically recorded in the French oyster industry since the early 1990s (OsHV-1 'reference'). From 2008, a new variant of ostreid herpesvirus (OsHV-1 mu Var) has emerged and seriously impacted oyster production in France and other European countries. Consequently, the presence of ostreid herpesviruses has been monitored in different oyster producing areas around the world. The present study compiles molecular data that are available from survey efforts and takes a biogeographical approach, in order to infer an origin for ostreid herpesviruses. The highest genotype diversity was found in East Asia, despite a lower survey effort in that area than in Europe. Genotype network analyses show that both populations of ostreid herpesviruses present in Europe (OsHV-1 'reference' and OsHV-1 mu Var) are closely related to genotypes recorded in Asia. Moreover, ostreid herpesviruses have been detected in wild and symptom-free populations of various Asian native Crassostrea species. In the rest of the world, ostreid herpesvirus genotypes were recorded from cultivated C. gigas, and mostly associated with mortality episodes. Results of this study are therefore highly suggestive of an Asian origin for these viruses, which can be pathogenic under farming conditions. It also highlights the risks of European stock improvements, by means of overseas shellfish imports.

Evolution of the extracellular matrix in deuterostomes and the influence of calcitropic hormones

Tese de dout., Biologia (Biologia Molecular), Faculdade de Ciências e Tecnologia, Univ. do Algarve, 2010

Development and standardization of a protocol for sperm cryopreservation of two important commercial oyster species

Dissertação de mestrado, Aquacultura e Pescas, Faculdade de Ciências e Tecnologia, Universidade do Algarve, 2015

Crescimento e qualidade microbiológica das ostras produzidas em cultivos multitróficos versus monocultivos

Dissertação de mestrado, Aquacultura e Pescas (Aquacultura), Faculdade de Ciências e Tecnologia, Universidade do Algarve, 2015

Resultados de la pesca exploratoria de 1979/80 y desembarque de cefalópodos pelagicos en el litoral peruano

El trabajo comprende un análisis de los desembarques de "ca amar" y "pota" desde 1964 a 1981 así como de los resultados de la pesca exploratoria de setiembre 1979 a abril 1 980. las principales especies de cafalópados que se comercializan en Perú bajo la nominación de calamares ( y calamaretes) pertenecen a la familia Loliginidae y de potas o jibias a la familia Ommastrephidae. El promedi o anual de desembarque de 1964 a 1971 de calamarés y potas fue de 243 y 313 toneladas respectivamente, de 1972 a 1981 continúa el desembarque regular de calamares pero no el de potas . Las mejores capturas de calamares y potas se producen en otoño durante los meses de mayo y junio y también en el verano durante los meses de enero y febrero . Casi la totalidad de desembarques de calamares se efectúan en el Callao, Huacho, Chimbote, Paita y el 78% de potas se desembarcan en el Callao y caletas aledañas. La pesca exploratoria de cefalópodos pelágicos efectuada principalmente a bordo del B/P japonés Rhyusho Maru Nº 25, de diciembre a abril 1980, cubrió todo el litoral peruano hasta las 500 mill as afuera. Se efectuaron 128 estaciones de pesca con el sistema y equipos especificas para la captura de calamares; se obtuvo una extracción de 18 toneladas de potas que correspondió a la especie oceánica Dosidicus gigas, con un promedi o de 140 kg por noche y amplitud entre 4 y 830 kg por noche de operación. Los niveles de la población de D. gigas durante la exploración estuvieron bajos, sin embargo las mejores concentraciones de esta especie se ubicaron en la zona norte a partir de las 30 millas hacia afuera en los meses de febrero y marzo( 246 y 224 kg/noche), observándose regu­lares focos a 350 millas afuera de Atico (16°10'8) en marzo (202 kg/noche) .

Crucero de investigaciones sobre el recurso calamar gigante o pota a bordo del BIC SNP-1. CR.9510-11 Chicama - Pto. Pizarro

Indica los acondicionamiento al BIC SNP-1 para la pesca del calamar y los resultados obtenidos entre la zona de Chicama hasta Pto. Pizarro, en octubre y noviembre de 1995. Asimismo, presenta los resultados de la aplicación del método de captura con máquinas calamareras, sistema de luces y sistema de anclaje y de los muestreos oceanográficos, acústicos y biológicos-pesqueros.

Investigación sobre el calamar gigante o pota en primavera 1996 en el área de Puerto Pizarro a Paita. Crucero BIC SNP-1 9609-10

Presenta los resultados de la prospección acústica pesquera, en la zona de Puerto Pizarro a Paita, hasta las 320 millas náuticas de distancia a la costa, del 25 de setiembre al 20 de Octubre 1996. El recurso se encontró muy disperso en casi toda el área prospectada, asociado a temperaturas superficiales y salinidades.

Crucero de investigación del calamar gigante BIC SNP-2 9903-04, 23 marzo al 12 abril 1999

Presenta los resultados del crucero de Investigación del calamar gigante, realizado a bordo del BIC SNP-2, del 23 de marzo al 12 de abril de 1999, de Puerto Pizarro al Callao, con el objeto de recopilar información actualizada sobre el estado biológico poblacional del recurso y las condiciones oceanográficas en el área y período de estudio.

Aspectos biológicos pesqueros de los recursos pelágicos durante el verano 1999. Crucero BIC BIC José Olaya Balandra 9902-03, de Tumbes a Tacna

Principales resultados de los aspectos biológicos pesqueros de las especies capturadas en los 336 lances de comprobación. Las especies capturadas fueron la anchoveta (Engraulis ringens), el camarón rojo o múnida (Pleuroncodes monodon), el bagre (Galeichthys peruvianus), la samasa (Anchoa nasus), el camotillo (Normanichthys crockeri), la caballa (Scomber japonicus), el falso volador (Prionotus stephanophrys) la pota (Dosidicus gigas), la sardina (Sardinops sagax) y el jurel (Trachurus picturatus murphyi), estos dos últimos fueron capturados en poca cantidad, y otra especies. La anchoveta se distribuyó ampliamente entre Pimentel y Callao; entre Callao y Bahía Independencia se localizó en la zona litoral en concentraciones dispersas y hacia el sur de Bahía Independencia, se le encontró con mucho menor frecuencia y dentro de las 10 mn de la costa. La estructura por tallas de anchoveta estuvo conformada por ejemplares juveniles y adultos, predominando ligeramente estos últimos. Las tallas de la sardina, el jurel y la caballa en el área evaluada, fueron principalmente de juveniles. El desove de verano de la anchoveta se desarrolló normalmente. Los adultos más jóvenes (12,0 a 14,0 cm longitud total) marcan notoriamente el pico del desove de verano; mientras que los individuos mayores se mantienen en este proceso por un tiempo más prolongado.