998 resultados para winged tree, floral elements


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Foi realizada a descrição morfológica das inflorescências, bem como das flores pistiladas e estaminadas, de uma população de Astrocaryum aculeatum Meyer, no Campus do Instituto Nacional de Pesquisas da Amazônia - INPA. A inflorescência é do tipo panícula de espigas, pedunculada, interfoliar e apresenta tamanho médio de 146 ± 20,3 cm. Uma bráctea lenhosa provida de espinhos em toda superfície externa protege a inflorescência. Estas apresentam cerca de 375 ± 49,5 ráquilas. Foi estimado de 500 a 1.200 flores pistiladas e 190.000 a 260.000 flores estaminadas por inflorescência. As flores estaminadas apresentam um padrão de cores que variam do vinho ao creme e também com tons mesclados de vinho e creme.

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A multilocus mixed-mating model was used to evaluate the mating system of a population of Couratari multiflora, an emergent tree species found in low densities (1 individual/10 ha) in lowland forests of central Amazonia. We surveyed and observed phenologically 41 trees in an area of 400 ha. From these, only four mother trees were analyzed here because few of them set fruits, which also suffered high predation. No difference was observed between the population multilocus outcrossing rate (t mp = 0.953 ± 0.040) and the average single locus rate (t sp = 0.968 ± 0.132). The four mother trees were highly outcrossed (t m ~ 1). Two out of five loci showed departures from the Hardy-Weinberg Equilibrium (HWE) expectations, and the same results occurred with the mixed-mating model. Besides the low number of trees analyzed, the proportion of loci in HWE suggests random mating in the population. However, the pollen pool was heterogeneous among families, probably due to both the small sample number and the flowering of trees at different times of the flowering season. Reproductive phenology of the population and the results presented here suggest, at least for part of the population, a long-distance pollen movement, around 1,000 m.

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Stomata are turgor-operated valves that control water loss and CO2 uptake during photosynthesis, and thereby water relation and plant biomass accumulation is closely related to stomatal functioning. The aims of this work were to document how stomata are distributed on the leaf surface and to determine if there is any significant variation in stomatal characteristics among Amazonian tree species, and finally to study the relationship between stomatal density (S D) and tree height. Thirty five trees (>17 m tall) of different species were selected. Stomatal type, density (S D), size (S S) and stomatal distribution on the leaf surface were determined using nail polish imprints taken from both leaf surfaces. Irrespective of tree species, stomata were located only on the abaxial surface (hypostomaty), with large variation in both S D and S S among species. S D ranged from 110 mm-2 in Neea altissima to 846 mm-2 in Qualea acuminata. However, in most species S D ranges between 271 and 543 mm-2, with a negative relationship between S D and S S. We also found a positive relationship between S D and tree height (r² = 0.14, p < 0.01), but no correlation was found between S D and leaf thickness. The most common stomatal type was anomocytic (37%), followed by paracytic (26%) and anisocytic (11%). We conclude that in Amazonian tree species, stomatal distribution on the leaf surface is a response most likely dependent on the genetic background of every species, rather than a reaction to environmental changes, and that somehow S D is influenced by environmental factors dependent on tree height.

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The high tree diversity and vast extent of Amazonian forests challenge our understanding of how tree species abundance and composition varies across this region. Information about these parameters, usually obtained from tree inventories plots, is essential for revealing patterns of tree diversity. Numerous tree inventories plots have been established in Amazonia, yet, tree species composition and diversity of white-sand and terra-firme forests of the upper Rio Negro still remain poorly understood. Here, we present data from eight new one-hectare tree inventories plots established in the upper Rio Negro; four of which were located in white-sand forests and four in terra-firme forests. Overall, we registered 4703 trees > 10 cm of diameter at breast height. These trees belong to 49 families, 215 genera, and 603 species. We found that tree communities of terra-firme and white-sand forests in the upper Rio Negro significantly differ from each other in their species composition. Tree communities of white-sand forests show a higher floristic similarity and lower diversity than those of terra-firme forests. We argue that mechanisms driving differences between tree communities of white-sand and terra-firme forests are related to habitat size, which ultimately influences large-scale and long-term evolutionary processes.

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A study was carried out to evaluate the association of levels of radioactivity, selenium and aflatoxin in shelled Brazil nuts, which were classified in different sizes, for export. The selenium determinations were performed by inductively coupled plasma optical emission spectrometry (LOQ = 3.0 µg g-1), and aflatoxins were detected by Liquid chromatography-mass spectrometry (LOQ = 0.85 µg kg-1), recovery rates were between 92 and 100%. Radioactivity was measured by high-resolution gamma spectrometry. The selenium mean concentration was (22.7 ± 7.4) µg g-1. (n = 30). Mean activities determined for the following radium isotopes were: 15.77 Bq kg-1 for 224Ra, 104.8 Bq kg-1 for 226Ra and 99.48 Bq kg-1 for 228Ra. For 226Ra, the levels did not vary significantly with nut sizes, although such differences were observed for 224Ra and 228Ra. There was no statistically significant association between the level of selenium and the activity of radionuclides, however, there was correlation between the radionuclides. Aflatoxins above the quantification limit were not found.

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The objective of this research was to describe the biological and morphometric aspects of the parica tree defoliator, Syssphinx molina (Cramer), and make recommendations about the insect rearing. The life cycle was 62.9 days with mean periods for the egg, larval, pre-pupal and pupal stages of 5.6, 31.1, 2.2 and 16.6 days respectively. The pupal viability was 60.5% for females and 48.6% for males. The sexual ratio was 0.5 with mean production of 182.3 ± 2.2 eggs per female and egg viability of 24.3%. The mean longevity was 7.9 ± 2 and 8.1 ± 3 days for females and males respectively. Other parameters were also observed and compared with description of other Saturniidae species.

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White sand forests, although low in nutrients, are characterized not only by several endemic species of plants but also by several monodominant species. In general, plants in this forest have noticeably thin stems. The aim of this work was to elaborate a parallel dichotomous key for the identification of Angiosperm tree species occurring on white sand forests at the Allpahuayo Mishana National Reserve, Loreto, Peru. We compiled a list of species from several publications in order to have the most comprehensive list of species that occur on white sand forest. We found 219 species of Angiosperm, the more abundant species were Pachira brevipes (26.27%), Caraipa utilis (17.90%), Dicymbe uaiparuensis (13.27%), Dendropanax umbellatus (3.28%), Sloanea spathulata (2.52%), Ternstroemia klugiana (2.30%), Haploclathra cordata (2.28%), Parkia igneiflora (1.20%), Emmotum floribundum (1.06%), Ravenia biramosa (1.04%) among others. Most species of white sand forests can be distinguished using characteristics of stems, branches and leaves. This key is very useful for the development of floristic inventories and related projects on white sand forests from Allpahuayo Mishana National Reserve.

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Species distribution modeling has relevant implications for the studies of biodiversity, decision making about conservation and knowledge about ecological requirements of the species. The aim of this study was to evaluate if the use of forest inventories can improve the estimation of occurrence probability, identify the limits of the potential distribution and habitat preference of a group of timber tree species. The environmental predictor variables were: elevation, slope, aspect, normalized difference vegetation index (NDVI) and height above the nearest drainage (HAND). To estimate the distribution of species we used the maximum entropy method (Maxent). In comparison with a random distribution, using topographic variables and vegetation index as features, the Maxent method predicted with an average accuracy of 86% the geographical distribution of studied species. The altitude and NDVI were the most important variables. There were limitations to the interpolation of the models for non-sampled locations and that are outside of the elevation gradient associated with the occurrence data in approximately 7% of the basin area. Ceiba pentandra (samaúma), Castilla ulei (caucho) and Hura crepitans (assacu) is more likely to occur in nearby water course areas. Clarisia racemosa (guariúba), Amburana acreana (cerejeira), Aspidosperma macrocarpon (pereiro), Apuleia leiocarpa (cumaru cetim), Aspidosperma parvifolium (amarelão) and Astronium lecointei (aroeira) can also occur in upland forest and well drained soils. This modeling approach has potential for application on other tropical species still less studied, especially those that are under pressure from logging.

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Dissertação de mestrado em Plant Molecular Biology, Biotechnology and Bioentrepeneurship

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A high-resolution mtDNA phylogenetic tree allowed us to look backward in time to investigate purifying selection. Purifying selection was very strong in the last 2,500 years, continuously eliminating pathogenic mutations back until the end of the Younger Dryas (∼11,000 years ago), when a large population expansion likely relaxed selection pressure. This was preceded by a phase of stable selection until another relaxation occurred in the out-of-Africa migration. Demography and selection are closely related: expansions led to relaxation of selection and higher pathogenicity mutations significantly decreased the growth of descendants. The only detectible positive selection was the recurrence of highly pathogenic nonsynonymous mutations (m.3394T>C-m.3397A>G-m.3398T>C) at interior branches of the tree, preventing the formation of a dinucleotide STR (TATATA) in the MT-ND1 gene. At the most recent time scale in 124 mother-children transmissions, purifying selection was detectable through the loss of mtDNA variants with high predicted pathogenicity. A few haplogroup-defining sites were also heteroplasmic, agreeing with a significant propensity in 349 positions in the phylogenetic tree to revert back to the ancestral variant. This nonrandom mutation property explains the observation of heteroplasmic mutations at some haplogroup-defining sites in sequencing datasets, which may not indicate poor quality as has been claimed.

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"Series title: Springerbriefs in applied sciences and technology, ISSN 2191-530X"

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Identificación y caracterización del problema: El fenotipo floral puede explicarse como respuesta adaptativa a los polinizadores. Sin embargo, está también influido por otros procesos como aislamiento geográfico, contexto histórico, efectos ambientales así como limitaciones filogenéticas y de desarrollo. Aunque las presiones selectivas ejercidas por un grupo funcional de polinizadores es supuestamente una característica prevalente que subyace a la evolución floral y especiación en los estudios de la biología evolutiva de las flores, la evidencia sobre importancia de los polinizadores como fuerzas moldeadoras del fenotipo floral es escasa y equívoca. Hipótesis Los patrones de variación de caracteres florales relacionados al ajuste flor-polinizador son explicados por la selección contemporánea y pasada ejercida por los polinizadores más eficientes. Objetivos: Estudiar la influencia de los polinizadores y de otros procesos como aislamiento geográfico, contexto histórico, efectos ambientales así como limitaciones filogenéticas y de desarrollo, como fuerzas moldeadoras del fenotipo floral dentro y entre poblaciones de una misma especie, así como entre especies diferentes. Materiales y métodos: Se encarará el estudio de sistemas plantas-polinizador sobre cuyo funcionamiento tenemos conocimientos previos y resultados publicados con aproximaciones que resultaron exitosas en otros estudios realizados por nosotros o con aproximaciones que son novedosas en los estudios de estos sistemas. Se integrarán aproximaciones de morfometría clásica y geométrica, de análisis filogenético y filogeográfico, análisis de contrastes independientes, de modelado predictivo de nicho, de selección e integración fenotípica en distintas especies o grupos de especies. Resultados esperados Los estudios de selección fenotípica deberán servir para demostrar si caracteres claves en el ajuste flor-polinizador son contemporáneamente blanco de la selección natural, si similar selección pasada ha dejado su impronta en la estructura de covariación (integración) y si esos caracteres son heredables. A nivel inter-poblacional, se espera demostrar que esta variación geográfica en atributos florales está relacionada con el ensamble de polinizadores cambiantes, y que esta variación se reflejada en la estructura genética geográfica, y que distintos escenarios selectivos (históricos y ecológicos como distintos ensambles de polinizadores) tienen consecuencias en los patrones de selección contemporánea (selección fenotípica) o pasada (integración). A nivel inter-específico, sobre estos antecedentes se plantean dos posibles situaciones de estudio en especies de plantas filogenéticamente hermanas que conviven y que ya sea, que comparten la misma especie de abeja polinizadora o que presentan dos sistemas de polinización contrastantes (aves o abejas) y forman una zona híbrida. Importancia del proyecto: Poder responder preguntas relevantes sobre biología evolutiva tomando como modelo al efecto selectivo de polinizadores sobre distintas especie de plantas nativas del Córdoba y otras regiones del país. Por otro lado, el conocimiento de los sistemas planta/polinizador impacta sobre la conservación de interacciones, el sustento de la biodiversidad. Esto contribuiría a la elaboración de protocolos de conservación de especies nativas del país.

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