737 resultados para CANNA CANNA-EDULIS


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Maracujá (do tupi mara Kuya, "fruto que serve" ou "alimento na cuia") é a denominação dada ao fruto produzido por plantas do gênero Passiflora da família Passifloraceae. Das cerca de 600 espécies de Passiflora, P. edulis f. flavicarpa (maracujá amarelo), P. edulis (maracujá roxo) e P. alata (maracujá doce) são responsáveis por 95% da área plantada no Brasil, o maior produtor mundial da fruta com 684.376 toneladas produzidas em 2008 (IBGE, 2009). Dentre os Estados brasileiros, o destaque é a Bahia, principal produtor com 275.445 t produzidas em 2008, seguido por Espírito Santo, Sergipe, Minas Gerais e São Paulo (IBGE,2009).

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Consorciacao com culturas de ciclo curto. consorciacao com culturas perenes. seringueira x cafeeiro. sistemas temporarios. Consorciacao do cafeeiro durante a formacao do seringal. Substituicao de cafezal em fim de ciclo por seringal. Sistemas permanentes. Seringal em renques no cafezal. Arborizacao do cafezal com seringueiras. Seringueira x cacaueira. Cacaueira x seringais velhos e desfolhados. Novos plantios consorciados de seringueira x cacaueiro. Seringueira x citros. Substituicao de pomares citricos decadentes por seringais. Consorciacao de citros durante a formacao do eringal. Consorciacao permanente de seringueira x citros. Seringueira x pimenteira-do-reino. Seringueira x palmeiras e plantas menos exigentes de luz. Seringueira x guaranazeiro. Seringueir-ras como componentes de quintais agroflorestais.

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2001

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2001

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Frutos do maracuja-doce de dez procedencias foram avaliados quanto a severidade da antracnose (Colletotrichum gloeosporioides Penz.) e quanto a perda de materia fresca em dois ambientes de armazenamento: camara fria ( 5 ºC e UR de 90%) e em ambiente de sala ( 23 +-1 ºC e UR de 65+- 5%). Plantas provenientes de frutos colhidos em estado nativo ou adquiridos nos mercados da Central de Abastecimento de São Paulo - CEAGESP, procedencias A, B, e C; Vicosa-MG, procedencia D; Tome-Acu-PA, procedencia E, Itacoatiara-AM, procedencia F, Ouro Preto d'Oeste-RO, procedencia G; Domingos Martins-ES, procedencia H; Pontes e Lacerda-MT, procedencia I; e Rondonopolis-MT, procedencia J foram estabelecidas no Distrito Federal. Apos as primeiras colheitas, a melhor planta de cada procedencia, selecionada pela maior taxa de vingamento, coloracao de casca, tamanho do fruto e menor espessura da casca, foi multiplicada por estaquia. Frutos de tres plantas de cada procedencia, obtidos por polinizacao natural, forma colhidos de vez e mantidos em caixas-padrao de papelao. As avalacoes forma efetuadas no dia da colheita (tempo zero), aos 3, 6, 9 e 12 dias apos, determinado-se o percentual de perda de materia fresca e a severidade da antracnose ( % da superficie do fruto ocupada por lesoes) e incidencia (% de frutos atacados) de outras doencas, aos 12 dias de armazenamento. As procedencias com menores indices de antracnose foram a I e a G, seguidas pela D e J. Os frutos armazenados em camaras fria foram menos afetados pela doenca. As procedencias G e A foram as que, ao final dos doze dias de armazenamento, perderam menos materia fresca sendo as perdas respectivamente de 16,68% e 17,86% em ambiente de sala e de 7,71% e 6,61% em camara fria. Considerando-se a media de todas as procedencias aos 12 dias de armazenamento, a menor perda de materia fresca ( 9, 78%) ocorre em camara fria, contra 22, 06% em ambiente de sala. As procedencias A, E, F, G e J perde menos materia fresca em ambiente natural que as demais.

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2007

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Ecosystem goods and services provided by estuarine and near coastal regions are being increasingly recognised for their immense value, as is the biodiversity in these areas and these near coastal communities have been identified as sentinels of climate change also. Population structure and reproductive biology of two bivalve molluscs, Cerastoderma edule and, Mytilus edulis were assessed at two study sites over a 16-month study period. Following an anomalously harsh winter, advancement of spawning time was observed in both species. Throughout Ireland and Europe the cockle has experienced mass surfacings in geographically distinct regions, and a concurrent study of cockles was undertaken to explore this phenomenon. Surfaced and buried cockles were collected on a monthly basis and their health compared. Age was highlighted as a source of variation between dying and healthy animals with a parasite threshold being reached possibly around age three. Local factors dominated when looking at the cause of surfacing at each site. The health of mussels was explored too on a temporal and seasonal basis in an attempt to assess what constitutes a healthy organism. In essence external drivers can tip the balance between “acceptable” levels of infection where the mussel can still function physiologically and “unacceptable” where prevalence and intensity of infection can result in physiological impairment at the individual and population level. Synecological studies of intertidal ecosystems are lacking, so all bivalves encountered during the sampling were assessed in terms of population structure, reproduction, and health. It became clear, that some parasites might specialize on one host species while others are not so specific in host choice. Furthermore the population genetics of the cockle, its parasite Meiogymnophallus minutus, and its hyperparasite Unikaryon legeri were examined too. A small nucleotide polymorphism was detected upon comparison of Ireland and Morocco.

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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.

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The problems of relating the results of experiments in the laboratory to events in nature are twofold: to equate the response to a single variable (hydrocarbons) with the natural variability in the biological material in a multivariate environment, and to consider whether the response established experimentally has any relevance to the animal's chances of survival and reproduction (i.e. its fitness) in the natural population. Recent studies of the effects of petroleum hydrocarbons on marine invertebrates are reviewed, with an emphasis on the physiological and cytochemical responses by bivalve molluscs. The dose-response relations that emerge suggest the intensity of the 'signal' that must be detected in nature if the chronic, sublethal effects of petroleum pollution are to be measured. The natural variability in these physiological and cytochemical processes are then reviewed and the main causes of variability in natural populations, both endogenous and exogenous, discussed. These results indicate the extent of the `noise' above which the signal from possible pollution effects must be detected. The results from recent field studies on the common mussel, Mytilus edulis, are discussed. The results are as complex as expected, but it proves possible to reduce the variance in the measured responses so that pollution effects, including those due to hydrocarbons, can be detected. The ecological consequences of the observed effects of petroleum hydrocarbons are then discussed in terms of reproductive effort and reproductive value. Considerable variation between populations exists here also and this can be used to help in the interpretation of the extent of the impact of the environment on the ecology of the population. The result is to place the findings of the laboratory experiments in an ecological context of natural variability and of the physiological costs of adaptation.

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A consideration of some physiological (rates of oxygen consumption, the scope for growth) and cellular (the cytochemical latency of a lysosomal enzyme) processes in bivalve molluscs suggests that animal size and seasonal changes related to the gametogenic cycle are important sources of natural variability. Correcting for size using regression techniques, and limiting measurements to one part of the gametogenic cycle, reduces observed natural variability considerably. Differences between populations are then still apparent, but the results of laboratory experiments with hydrocarbons from crude oil suggest that it should be possible to detect sub-lethal effects due to pollution (the ‘signal’) in the presence of the remaining natural variability (the ‘noise’). Statistical considerations, taken together with results from current studies on Mytilus edulis and Scobicularia plana, indicate that sample sizes of 10–15 individuals should suffice for the detection of possible pollution effects. The physiological effects to be expected in the presence of sub-lethal levels of polluting hydrocarbons are on a scaie that can cause significant ecological damage to a population through a reduction in fecundity and the residual reproductive value of the individuals.

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Structural changes were observed in the digestive tubule epithelial cells of Mytilus edulis following long-term exposure to the water accommodated fraction (WAF) of North Sea crude oil (30 μg · l−1 total oil derived aromatic hydrocarbons). The changes observed involved a reduction in the height of the digestive cells beyond that demonstrated in a normal feeding cycle. In addition there was a loss of the normal synchrony of the digestive cells to a point where nearly all the tubules exhibited an appearance similar to that which is usually termed ‘reconstituting’. These alterations were quantified using an image analysis technique and the mean height of the digestive cells used as an index of digestive function or state. Long-term exposure also induced a radical alteration of the structure of secondary lysosomes within the digestive cells, resulting in the formation of large lysosomes, believed to be autolysosomes. Stereological analyses showed that these lysosomes are reduced in numbers and greatly increased in volume in comparison with controls. There is a concomitant increase in surface area of lysosomes per unit volume of digestive cell compared with control conditions. These alterations are indicative of fundamental changes in secondary lysosomal function involving an autophagic response to oil derived hydrocarbons. which would contribute to the reduction of digestive cell cytoplasm. These cellular alterations are discussed in terms of their use as indices of cell injury, in response to oil.