578 resultados para Canavalia maritima


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Las dos grandes fuentes de alimentación animal son: energética que comúnmente esta dada por las gramíneas y proteica, la cual puede ser suplementada por diferentes vías, pero las mas simple y que la naturaleza la provee es a través de las leguminosas, producto de la asociación con bacterias del género Rhizobium, que les permite fijar nitrógeno atmosférico. Los estudio hechos de leguminosas al momento han sido muy pocos, y cuando se han hecho se ha centrado únicamente en zonas del caribe con alta precipitación y suelos ácidos. Por lo que con el objeto de conocer el comportamiento de adaptación agronómico y productivo de 9 especies de leguminosas consideradas como forrajeras en el municipio de Muy Muy, se realizó el presente estudio en la finca “La Cruz” propiedad del señor Santiago Espino, ubicada en el km 153 de la carretera Muy Muy-Matiguás, en la comunidad de “Aguas Calientes”, zona baja del municipio de Muy Muy, Matagalpa, localizado en las coordenadas geográficas 12º 45 ́48” latitud Norte y 85º 37 ́36”longitud Oeste, a una altitud de unos 286msnmy con una temperatura promedio anual de 25.0°C. se estableció el experimento de campo el 4 de Junio del 2007. Utilizándose un Diseño de Bloques Completos al Azar (BCA), con nueve tratamientos (especies evaluadas: Centrosema plumieri cv DICTA, Clitoria ternatea cv CEVAS, Canavalia brasiliensis CIAT 1700, Clitoria ternatea CV DICTA, Canavalia ensiformis, Lablab purpureus, Vigna unguiculata CIAT9611, Vigna unguiculata CIAT390-2 y Stylosanthes guianensis CIAT2243). Se midieron 9 variables: sobrevivencia, altura, vigor, cobertura, cobertura de maleza, suelo descubierto, incidencia de plagas, incidencia de enfermedades y producción de biomasa seca, además se realizó análisis de la composición química a ocho de las especies en estudio. S.guianensis 2243 presentó el mejor comportamiento agronómico, superando al resto de especies en casi todas las variables en estudio, salvo el caso de altura donde fue superada por C. brasiliensis 1700 con 95.5 cm y en suelo descubierto por C. plumieri DICTA con 4.38%. En sobrevivencia Stylo alcanzó un 100%, con cobertura de 76.25%, menor incidencia de plagas y enfermedades (0%) y ponderación en vigor de 4.9. Además S.guianensis 2243 presentó el mejor comportamiento en producción de biomasa seca con 3717.02 kg ha-1, seguida de C. plumieriDICTA con 1486.38 kg ha-1. La especie de menor comportamiento adaptativo fue V. unguiculata 9611, y en producción de biomasa L. purpureus con 206.82 kg ha-1. C. ensiformis presento mejor contenido proteico con 26.20% y C. ternateaCEVAS en la porción digerible con 85.71%, la de menor calidad fue S.guianensis 2243 con 13.26% de proteína y 54.59% de porción digerible. Aun con los resultados de calidad se considera que S. guianensis2243 es una especie promisoria para estas condiciones por su a daptabilidad y producción de biomasa, y calidad y a las especies C. plumieriDICTA y C. ternateaCEVAS por su calidad nutritiva, adaptación y producciónde biomasa.

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El presente estudio forma parte del trabajo conjunto del Centro Internacional de Agricultura Tropical (CIAT), el Programa de Investigación sobre Cambio Climático, Agricultura y Seguridad Alimentaria (CCAFS) y la Central de Cooperativas Cafetaleras del Norte (CECOCAFEN). Se identificaron las prácticas de adaptación al cambio climático que se están implementando en tres fincas del departamento de Matagalpa y se analizó el impacto de las mismas a nivel socioeconómico y ambiental. Según el estudio Tortillas en el Comal (TOR – por sus siglas en inglés), se espera un aumento en las temperaturas medias anuales (alrededor de 1° C en la década de 2020 y 2° C en la década de 2050). Las temperaturas mínimas y máximas diarias serán más altas. Habrá un déficit creciente del agua debido a una menor precipitación y altas tasas de evap otranspiración de las plantas (...) el déficit hídrico del suelo que va a empeorar el estrés por calor para las plantas, reducirá significativamente los rendimientos y representa una grave amenaza para la seguridad alimentaria. (Eitzinger et al., 2012). Sin embargo, se ha logrado determinar que las prácticas de adaptación al cambio climático implementadas por los productores han tenido un impacto positivo. A nivel social, la diversificación de los medios de vida permite el abastecimiento alimentario suficiente para contrarrestar la problemática de los meses de escasez en las zonas cafetaleras. A nivel económico, la cosecha de agua y las estrategias de alimentación de verano en bovinos aseguran la producción de lácteos y carnes aún en tiempo de sequía en las zonas ganaderas. Y, finalmente a nivel ambiental, se ha mejorado la calidad del suelo mediante el establecimiento de sistemas agroforestales en café y cacao y el uso de Canavalia ensiformis para la recuperación de suelos.

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对百里香 (Thymusserpyllum )、平车前 (Plantagodepressa)、盐生车前 (P maritima)、野亚麻(Linumstelleroides)进行了粘液繁殖体粘液情况比较 .以在水浸和浇水条件下植物种子粘沙量的多少衡量粘液量 .结果表明 ,对于不同浸水时间处理 ,野亚麻和平车前未表现明显差异 ,盐生车前和百里香有随浸泡时间加长而粘液溶出量增多的趋势 .对于不同浇水量处理 ,4种植物均有随浇水量增多而粘液增多的倾向 .浸泡 80min后 ,盐生车前种子的粘液粘沙使重量达原重的 6 0多倍 ,平车前种子达原重的 10倍左右 ,百里香和野亚麻种子达原重的 4~ 6倍左右 .浇水 8mm后 ,盐生车前种子的粘液粘沙使重量达原重的 2 0多倍 ,平车前种子达原重的 6~ 10倍左右 ,百里香和野亚麻种子达原重的 2~ 7倍左右 .将各种处理平均 ,得到各种植物粘沙种子百分率为 :野亚麻 6 7 7% ,百里香 94 5 % ,平车前 97 7% ,盐生车前 99 5 % .

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Vibrio harveyi is an important marine pathogen that can infect a number of aquaculture species. V. harveyi degQ (degQ(Vh)), the gene encoding a DegQ homologue, was cloned from T4, a pathogenic V. harveyi strain isolated from diseased fish. DegQ(Vh) was closely related to the HtrA family members identified in other Vibrio species and could complement the temperature-sensitive phenotype of an Escherichia coli strain defective in degP. Expression of degQVh in T4 was modulated by temperature, possibly through the sigma(E)-like factor. Enzymatic analyses demonstrated that the recombinant DegQVh protein expressed in and purified from E. coli was an active serine protease whose activity required the integrity of the catalytic site and the PDZ domains. The optimal temperature and pH of the recombinant DegQVh protein were 50 C and pH 8.0. A vaccination study indicated that the purified recombinant DegQVh was a protective immunogen that could confer protection upon fish against infection by V. harveyi. In order to improve the efficiency of DegQVh as a vaccine, a genetic construct in the form of the plasmid pAQ1 was built, in which the DNA encoding the processed DegQVh protein was fused with the DNA encoding the secretion region of AgaV, an extracellular beta-agarase. The E.coli strain harboring pAQ1 could express and secrete the chimeric DegQVh protein into the culture supernatant. Vaccination of fish with viable E. coli expressing chimeric degQ(Vh) significantly (P < 0.001) enhanced the survival of fish against V. harveyi challenge, which was possibly due to the relatively prolonged exposure of the immune system to the recombinant antigen produced constitutively, albeit at a gradually decreasing level, by the carrier strain.

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Vibrio harveyi is an important marine pathogen that can infect a number of aquaculture species. V. harveyi degQ (degQ(Vh)), the gene encoding a DegQ homologue, was cloned from T4, a pathogenic V. harveyi strain isolated from diseased fish. DegQ(Vh) was closely related to the HtrA family members identified in other Vibrio species and could complement the temperature-sensitive phenotype of an Escherichia coli strain defective in degP. Expression of degQVh in T4 was modulated by temperature, possibly through the sigma(E)-like factor. Enzymatic analyses demonstrated that the recombinant DegQVh protein expressed in and purified from E. coli was an active serine protease whose activity required the integrity of the catalytic site and the PDZ domains. The optimal temperature and pH of the recombinant DegQVh protein were 50 C and pH 8.0. A vaccination study indicated that the purified recombinant DegQVh was a protective immunogen that could confer protection upon fish against infection by V. harveyi. In order to improve the efficiency of DegQVh as a vaccine, a genetic construct in the form of the plasmid pAQ1 was built, in which the DNA encoding the processed DegQVh protein was fused with the DNA encoding the secretion region of AgaV, an extracellular beta-agarase. The E.coli strain harboring pAQ1 could express and secrete the chimeric DegQVh protein into the culture supernatant. Vaccination of fish with viable E. coli expressing chimeric degQ(Vh) significantly (P < 0.001) enhanced the survival of fish against V. harveyi challenge, which was possibly due to the relatively prolonged exposure of the immune system to the recombinant antigen produced constitutively, albeit at a gradually decreasing level, by the carrier strain.

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As leguminosas utilizadas de forma intercalada nas culturas possuem a vantagem de incorporarem nitrogênio via fixação biológica de N2 atmosférico, permitemirem a reciclagem de nutrientes das camadas mais profundas e fornecemrem abrigo, alimento e locais de refúgio para os inimigos naturais. O grande desafio da agricultura moderna é identificar as melhores práticas de manejo ambiental dos agroecossistemas que estimulem a biodiversidade e os processos ecológicos que favoreçam a sustentabilidade desses sistemas por meio da geração de serviços ambientais. Na cultura dos citros, o feijão-de-porco Canavalia ensiformes (L.) tem sido utilizado nas entrelinhas do pomar visando ao manejo do solo no controle de plantas vegetação espontânea e para minimizar problemas de compactação nas entrelinhas da cultura aumentando a macroporosidade e disponibilidade da água no solo

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O trabalho objetiva definir a melhor época de plantio de Crotalaria juncea, feijão de porco (Canavalia ensiformis) e guandu (Cajanus cajan) em relação ao plantio do milho e seu efeito sobre a produção de grãos desta cultura sobre a produção de biomassa das leguminosas mais milho para adição ao solo como adubo verde.

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Pronounced changes have occurred in the fisheries, plankton and benthos of the North Sea over the last five decades. Attribution of the relative contribution of anthropogenic versus natural hydrometeorological modulation to these changes is still unclear. As a background a summary history of our understanding of the state of health of the North Sea is outlined. We then focus on two contrasting periods in the North Sea, one between 1978-82 (cold) and the other post 1987 (warm) when pronounced alterations in many ecosystem characteristics occurred. The scale of the changes in the second of these periods is sufficiently large and wide ranging for it to have been termed a regime shift. A combination of local, regional and far field hydrometeorological forcing, and in particular variability in oceanic inflow, is believed to be responsible for the observed changes. Finally attention is drawn to the poor status of North Sea fish stocks where 7 stocks are documented as being fished outside safe biological limits. This situation is primarily believed to be a consequence of overfishing, but may have been exacerbated by environmental change.

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This project was commissioned to generate an improved understanding of the sensitivities of seagrass habitats to pressures associated with human activities in the marine environment - to provide an evidence base to facilitate and support management advice for Marine Protected Areas; development of UK marine monitoring and assessment, and conservation advice to offshore marine industries. Seagrass bed habitats are identified as a Priority Marine Feature (PMF) under the Marine (Scotland) Act 2010, they are also included on the OSPAR list of threatened and declining species and habitats, and are a Habitat of Principle Importance (HPI) under the Natural Environment and Rural Communities (NERC) Act 2006, in England and Wales. The purpose of this project was to produce sensitivity assessments with supporting evidence for the HPI, OSPAR and PMF seagrass/Zostera bed habitat definitions, clearly documenting the evidence behind the assessments and any differences between assessments. Nineteen pressures, falling in five categories - biological, hydrological, physical damage, physical loss, and pollution and other chemical changes - were assessed in this report. Assessments were based on the three British seagrasses Zostera marina, Z. noltei and Ruppia maritima. Z. marina var. angustifolia was considered to be a subspecies of Z. marina but it was specified where studies had considered it as a species in its own rights. Where possible other components of the community were investigated but the basis of the assessment focused on seagrass species. To develop each sensitivity assessment, the resistance and resilience of the key elements were assessed against the pressure benchmark using the available evidence. The benchmarks were designed to provide a ‘standard’ level of pressure against which to assess sensitivity. Overall, seagrass beds were highly sensitive to a number of human activities: • penetration or disturbance of the substratum below the surface; • habitat structure changes – removal of substratum; • physical change to another sediment type; • physical loss of habitat; • siltation rate changes including and smothering; and • changes in suspended solids. High sensitivity was recorded for pressures which directly impacted the factors that limit seagrass growth and health such as light availability. Physical pressures that caused mechanical modification of the sediment, and hence damage to roots and leaves, also resulted in high sensitivity. Seagrass beds were assessed as ‘not sensitive’ to microbial pathogens or ‘removal of target species’. These assessments were based on the benchmarks used. Z. marina is known to be sensitive to Labyrinthula zosterae but this was not included in the benchmark used. Similarly, ‘removal of target species’ addresses only the biological effects of removal and not the physical effects of the process used. For example, seagrass beds are probably not sensitive to the removal of scallops found within the bed but are highly sensitive to the effects of dredging for scallops, as assessed under the pressure penetration or disturbance of the substratum below the surface‘. This is also an example of a synergistic effect Assessing the sensitivity of seagrass bed biotopes to pressures associated with marine activities between pressures. Where possible, synergistic effects were highlighted but synergistic and cumulative effects are outside the scope off this study. The report found that no distinct differences in sensitivity exist between the HPI, PMF and OSPAR definitions. Individual biotopes do however have different sensitivities to pressures. These differences were determined by the species affected, the position of the habitat on the shore and the sediment type. For instance evidence showed that beds growing in soft and muddy sand were more vulnerable to physical damage than beds on harder, more compact substratum. Temporal effects can also influence the sensitivity of seagrass beds. On a seasonal time frame, physical damage to roots and leaves occurring in the reproductive season (summer months) will have a greater impact than damage in winter. On a daily basis, the tidal regime could accentuate or attenuate the effects of pressures depending on high and low tide. A variety of factors must therefore be taken into account in order to assess the sensitivity of a particular seagrass habitat at any location. No clear difference in resilience was established across the three seagrass definitions assessed in this report. The resilience of seagrass beds and the ability to recover from human induced pressures is a combination of the environmental conditions of the site, growth rates of the seagrass, the frequency and the intensity of the disturbance. This highlights the importance of considering the species affected as well as the ecology of the seagrass bed, the environmental conditions and the types and nature of activities giving rise to the pressure and the effects of that pressure. For example, pressures that result in sediment modification (e.g. pitting or erosion), sediment change or removal, prolong recovery. Therefore, the resilience of each biotope and habitat definitions is discussed for each pressure. Using a clearly documented, evidence based approach to create sensitivity assessments allows the assessment 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. 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 seagrass habitats may 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.

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O sistema lagunar, conhecido vulgarmente por Ria Formosa, desenvolve-se na costa meridional Portuguesa, desde o Ancão a ocidente até Cacela a oriente. Com extensão, de aproximadamente 55 km, apresenta a sua maior largura, de 6 km, no sector Norte-Sul entre Faro e o Cabo de Santa Maria. Este sistema é um conjunto de ilhas-barreira que proteje a zona lagunar adjacente à plataforma litoral algarvia, da invasão marinha. A área total do Parque Natural da Ria Formosa é aproximadamente de 163 km2, sendo 48 km2 cobertos por sapal e 32 km2 ocupados por canais, esteiros e baixios (Teixeira & Alvim, 1978). Durante as marés vivas, as áreas intertidais expostas são de aproximadamente 50 km2. Estas áreas são predominantemente cobertas por plantas de sapal (Spartina maritima), angiospérmicas marinhas (Zostera e Cymodocea) e mantos de macroalgas (Entermorpha, Ulva e Fucus). 20 km2 do sistema são ocupados por salinas e aquaculturas (CCRA, 1984).

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Dissertação de mestrado, Biologia Marinha, Faculdade de Ciências e Tecnologia, Universidade do Algarve, 2015

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Dissertação de mestrado, Engenharia Biológica, Faculdade de Ciências e Tecnologia, Universidade do Algarve, 2015

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Tese de doutoramento, Geologia (Geoquímica), Universidade de Lisboa, Faculdade de Ciências, 2016

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Tese de doutoramento, Farmácia (Toxicologia), Universidade de Lisboa, Faculdade de Farmácia, 2016