139 resultados para Commelina virginica


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Um dos herbicidas mais utilizados para o controle de plantas daninhas em pós-emergência nos pomares cítricos paulistas é o glyphosate. No entanto, este herbicida aplicado isoladamente e nas doses recomendadas, tem proporcionado seleção da planta daninha trapoeraba (Commelina virginica L.), devido à grande tolerância da mesma, somada à eficiente eliminação das demais espécies da comunidade infestante. em vista disso, e pela falta de opções , faz-se necessária a pesquisa de outros herbicidas ou misturas de herbicidas que sejam eficientes no controle da trapoeraba, de baixa toxicidade para os aplicadores, sistêmicos, e que sejam seletivos às plantas cítricas. O presente trabalho foi desenvolvido com o objetivo de estudar a eficiência da mistura pronta dos herbicidas glyphosate + 2,4-D amina no controle da trapoeraba em citros [Citrus sinensis (L.) Osbeck], em comparação com estes mesmos herbicidas aplicados isoladamente, bem como os possíveis efeitos fitotóxicos da mesma à cultura. O experimento foi instalado na região de Catanduva-SP, em um pomar de laranja Pera clone Rio, enxertada sobre limão Cravo, com dez anos de idade, plantado em um espaçamento de 8,0 x 6,5 m. A aplicação dos herbicidas foi realizada em 20 de fevereiro de 1991, de forma dirigida, em pós-emergência tardia da trapoeraba, quando a mesma já florescia e tinha altura variável entre 15 e 60 cm. A análise e interpretação dos resultados obtidos mostraram que a mistura pronta de glyphosate + 2,4-D apresenta um controle superior da trapoeraba em relação aos produtos aplicados isoladamente, não havendo diferenças significativas no controle para doses superiores a 0,60 + 0,80 kg i.a./ha. Os dados obtidos reforçam a teoria de sinergismo entre os dois produtos. em nenhum dos tratamentos foi verificado sintomas visuais de intoxicação nas laranjeiras.

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The morphology of 20 species of weeds that occur in the most common crops in Maringá, Paraná State, Brazil and adjacent regions were described at early developmental stages, in order to identify the species in the field and provide information for taxonomic and ecological works. Sixteen species featured epigeal-foliaceous seedlings. The seedling in Cardiospenuum halicacabum is epigeal-fleshy; in Cenchrus echinatus and Digitaria horizontalis it is hypogeal and in Commelina virginica is epigeal-cryptocotyledonar. The differentiation of the first eophyll occurred within ten (Digitaria horizontalis) to 35 days (Bidens pilosa) and the first metaphyll appeared within 22 (Commelina virginica) to 49 days (Acanthospenuum australe). The number of eophylls varied from one to four, and the phyllotaxis varied from alternate to opposite.

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La especie Commelina bengalensis L. es una maleza de alto riesgo y reconocida agresividad, la cual, conforme legislación vigente en Nicaragua, tiene restringida la introducción al país. En vista de lo anterior, se llevó a cabo un estudio con el propósito de determinar la presencia-ausencia de dicha especie en la región sur-central y sur de Nicaragua, y en caso de ausencia, realizar un análisis de riesgo de introducción de la especie a través de la importación de semilla de pastos. El estudio se llevó a cabo en los departamentos de Boaco, Chontales, Rivas y el municipio de Nueva Guinea. El estudio es de naturaleza no experimental, de corte trasversal. En un periodo de 15 días, entre el 15 de marzo y el 30 de marzo del año 2012 se llevaron a cabo muestreos sistemáticos en pastizales de 14 fincas ganaderas en las regiones mencionadas. La información obtenida fue presencia o ausencia de la especie en mención, e información referente a otras especies del genero Commelina , con el propósito de corroborar o descartar la presencia de la especie. Posteriormente, en vista de la ausencia de la especie en los campos muestreados, en trabajo de gabinete se realizó una revisión documental con el propósito de hacer una evaluación del riesgo de introducción de la especie. Los resultados muestran ausencia de la especie. Durante el estudio fue posible determinar la presencia de las especies C . diffusa y C . erecta, las cuales muestras similitudes con C . benghalensis, sin embargo, particularidades morfológicas de esta última permiten descartar que se trate de dicha especie. Para evitar la introducción y establecimiento de C . benghalensis se debe exigir que las semillas de pastos importadas provengan de sitios libres de la especie, y donde se realice un manejo fitosanitario que garantice que el producto esté libre de semilla de la especie, realizar programa de verificación en los sitios de origen para determinar la procedencia de las semillas, así como cumplimiento de los requisitos que se establecen en programas de producción de semillas, exigir certificado fitosanitario internacional que indique que el producto proviene de áreas libres la maleza y localmente realizar inspección, muestreo y análisis de laboratorio para determinar la ausencia o presencia de la maleza.

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Considerations to introduce the Suminoe or Asian oyster Crassostrea ariakensis along the East Coast have raised many questions regarding ecology, economics, and human health. To date, research has focused primarily on the ecological and socioeconomic implications of this initiative, yet few studies have assessed its potential impact on public health. Our work compares the rates of bioaccumulation, depuration and post harvest decay of indicator organisms (such as E. coli) and Vibrio sp. between Crassostrea virginica and Crassostrea ariakensis in the laboratory. Preliminary results suggest that the rates of bioaccumulation of E. coli in Crassostrea ariakensis were significantly lower than those for Crassostrea virginica, depuration of E. coli was variable between the two species, and Crassostrea ariakensis post harvest decay rates of Vibrio sp. were significantly lower than Crassostrea virginica. This research provides coastal managers with insight into the response of Crassostrea ariakensis to bacteria, an important consideration for determining appropriate management strategies for this species. Further field-based studies will be necessary to elucidate the mechanisms responsible for the differences in rates of bioaccumulation and depuration. (PDF contains 40 pages)

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Abstract—In the first of two companion papers, a 54-yr time series for the oyster population in the New Jersey waters of Delaware Bay was analyzed to develop biological relationships necessary to evaluate maximum sustainable yield (MSY) reference points and to consider how multiple stable points affect reference point-based management. The time series encompassed two regime shifts, one circa 1970 that ushered in a 15-yr period of high abundance, and a second in 1985 that ushered in a 20-yr period of low abundance. The intervening and succeeding periods have the attributes of alternate stable states. The biological relationships between abundance, recruitment, and mortality were unusual in four ways. First, the broodstock–recruitment relationship at low abundance may have been driven more by the provision of settlement sites for larvae by the adults than by fecundity. Second, the natural mortality rate was temporally unstable and bore a nonlinear relationship to abundance. Third, combined high abundance and low mortality, though likely requiring favorable environmental conditions, seemed also to be a self-reinforcing phenomenon. As a consequence, the abundance –mortality relationship exhibited both compensatory and depensatory components. Fourth, the geographic distribution of the stock was intertwined with abundance and mortality, such that interrelationships were functions both of spatial organization and inherent populatio

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California, in response to health concerns, initiated a program on 1 March 1991 which required anyone selling eastern oysters, Crassostrea virginica, from the Gulf of Mexico area to notify potential consumers that there was a risk in consuming them raw. This mandatory warning, followed shortly thereafter by a similar warning in other states, including Louisiana and Florida, received extensive press cover-age throughout the country and particularly in the Gulf area. This paper examines the extent to which the demand for Gulf-area oysters has been reduced as a result of mandatory warning labels and negative publicity. In general, the results suggest that since 1991 the “summer” dockside price has been reduced by about 50% as a result of warning labels and associated negative publicity, while the “winter” dockside price has been reduced by about 30%.

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Chromosome identification is an essential step in genomic research, which so far has not been possible in oysters. We tested bacteriophage P1 clones for chromosomal identification in the eastern oyster Crassostrea virginica, using fluorescence in situ hybridization (FISH). P1 clones were labeled with digoxigenin-11-dUTP using nick translation. Hybridization was detected with fluorescein-isothiocyanate-labeled anti-digoxigenin antibodies and amplified with 2 layers of antibodies. Nine of the 21 P1 clones tested produced clear and consistent FISH signals when Cot-1 DNA was used as a blocking agent against repetitive sequences. Karyotypic analysis and cohybridization positively assigned the 9 P1 clones to 7 chromosomes. The remaining 3 chromosomes can be separated by size and arm ratio. Five of the 9 P1 clones were sequenced at both ends, providing sequence-tagged sites that can be used to integrate linkage and cytogenetic maps. One sequence is part of the bone morphogenetic protein type 1b receptor, a member of the transforming growth factor superfamily, and mapped to the telomeric region of the long arm of chromosome 2. This study shows that large-insert clones such as P1 are useful as chromosome-specific FISH probes and for gene mapping in oysters.

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Chromosomal location of the 5S ribosomal RNA gene was studied in the eastern oyster, Crassostrea virginica Gmelin. using fluorescence in situ hybridization (FISH). Metaphase chromosomes were obtained from early embryos, and the FISH probe was made by PCR (polymerase chain reaction) amplification of the 5S rRNA gene and labeled by incorporation of digoxigenin-1 1-dUTP during PCR. Hybridization was detected with fluorescein-labeled antidigoxigenin antibodies. Two pairs of FISH signals were observed on metaphase chromosomes. Karyotypic analysis showed that the 5S rRNA gene cluster is interstitially located on short arms of chromosomes 5 and 6. On chromosome 5, the 5S rRNA genes were located immediately next to the centromere, whereas on chromosome 6, they were located approximately half way between the telomere and the centromere. Chromosomes of C. virginica are difficult to identify because of their similarities in size and arm ratio, and the chromosomal location of 5S rRNA genes provides unambiguous identification of chromosomes 5 and 6. Previous studies have mapped the major rRNA gene cluster (18S-5.8S-28S) to chromosome 2. and this study shows that the 5S rRNA gene cluster is not linked to the major rRNA genes and duplicated during evolution.

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A model to estimate the mean monthly growth of Crassostrea virginica oysters in Chesapeake Bay was developed. This model is based on the classic von Bertalanffy growth function, however the growth constant is changed every monthly timestep in response to short term changes in temperature and salinity. Using a dynamically varying growth constant allows the model to capture seasonal oscillations in growth, and growth responses to changing environmental conditions that previous applications of the von Bertalanffy model do not capture. This model is further expanded to include an estimation of Perkinsus marinus impacts on growth rates as well as estimations of ecosystem services provided by a restored oyster bar over time. The model was validated by comparing growth estimates from the model to oyster shell height observations from a variety of restoration sites in the upper Chesapeake Bay. Without using the P. marinus impact on growth, the model consistently overestimates mean oyster growth. However, when P. marinus effects are included in the model, the model estimates match the observed mean shell height closely for at least the first 3 years of growth. The estimates of ecosystem services suggested by this model imply that even with high levels of mortality on an oyster reef, the ecosystem services provided by that reef can still be maintained by growth for several years. Because larger oyster filter more water than smaller ones, larger oysters contribute more to the filtration and nutrient removal ecosystem services of the reef. Therefore a reef with an abundance of larger oysters will provide better filtration and nutrient removal. This implies that if an oyster restoration project is trying to improve water quality through oyster filtration, it is important to maintain the larger older oysters on the reef.