920 resultados para PERSISTENCE LENGTH


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Este trabajo tiene como objetivos contribuir al conocimiento del proceso de alfabetización temprana en español en niños de sectores sociales desfavorecidos, y analizar los resultados de la implementación de un programa destinado al desarrollo de habilidades y conocimientos relativos a la lectura y la escritura inicial. El tipo de intervención propuesta, surge del programa ECOS , ya probado en español, pero no replicado suficientemente en niños de edades preescolares. Se ha estudiado el impacto de la aplicación de dicho programa, destinado a niños de 4, 5 y 6 años de edad, pertenecientes a sectores en desventaja socio económica, que concurrían a jardines de infantes de la Provincia de Buenos Aires (Argentina). Esta tesis se enmarca en los modelos de investigación proporcionados desde la Psicología Cognitiva y la corriente sociocultural, y sustenta la hipótesis de que el presente programa incrementa, en mayor medida que la curricula escolar las habilidades de conciencia fonológica, el reconocimiento y escritura de palabras y textos, así como también las habilidades de comprensión y producción oral de textos narrativos, en el corto y mediano plazo. Su originalidad reside en la especificidad del programa seleccionado y en haber considerado de manera conjunta la evaluación de su impacto, a través de un seguimiento longitudinal, que permitió no sólo verificar la persistencia de sus efectos a mediano plazo, sino también las relaciones que guardan entre sí las variables evaluadas, el poder predictivo de unas sobre otras, el momento en el que se produce el impacto y sobre cuáles de las variables y el tamaño de ese impacto. La investigación se realizó comparando el desempeño de dos grupos de niños uno experimental en el cual se aplicó dicho programa y uno control. Al inicio de la investigación los niños fueron homologados en cuanto al estrato social de procedencia (identificado por el nivel educacional y ocupacional de los padres), a las características de los establecimientos educativos a los que concurrían y a la de los contextos alfabetizadores hogareños así como respecto de sus conocimientos y habilidades iniciales. Las variables a ser consideradas en la evaluación de los desempeños fueron las siguientes: habilidades de conciencia fonológica, conocimientos sobre material impreso y sobre el sistema de escritura, lectura y escritura de palabras de diferente longitud y complejidad, lectura de pseudopalabras, lectura y escritura de textos y comprensión y renarración oral de textos narrativos. Los niños fueron evaluados en cuatro oportunidades diferentes, comparándose los desempeños de ambos grupos en el transcurso de dos años y medio: Se aplicó un modelo de medidas repetidas y se calculó el estadístico Effect Size para todas las variables al finalizar la intervención y mediano plazo. Las conclusiones extraídas de esta investigación ponen en evidencia el impacto positivo del programa de intervención. A mediano plazo se verifica una diferencia promedio de alrededor del 30 entre los niños de ambos grupos, en los porcentajes de aciertos en las pruebas que evalúan las habilidades de conciencia fonológica, lectura y escritura de palabras y comprensión de textos

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Acoustic estimates of herring and blue whiting abundance were obtained during the surveys using the Simrad ER60 scientific echosounder. The allocation of NASC-values to herring, blue whiting and other acoustic targets were based on the composition of the trawl catches and the appearance of echo recordings. To estimate the abundance, the allocated NASC -values were averaged for ICES-squares (0.5° latitude by 1° longitude). For each statistical square, the unit area density of fish (rA) in number per square nautical mile (N*nm-2) was calculated using standard equations (Foote et al., 1987; Toresen et al., 1998). To estimate the total abundance of fish, the unit area abundance for each statistical square was multiplied by the number of square nautical miles in each statistical square and then summed for all the statistical squares within defined subareas and over the total area. Biomass estimation was calculated by multiplying abundance in numbers by the average weight of the fish in each statistical square then summing all squares within defined subareas and over the total area. The Norwegian BEAM soft-ware (Totland and Godø 2001) was used to make estimates of total biomass.

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Acoustic estimates of herring and blue whiting abundance were obtained during the surveys using the Simrad ER60 scientific echosounder. The allocation of NASC-values to herring, blue whiting and other acoustic targets were based on the composition of the trawl catches and the appearance of echo recordings. To estimate the abundance, the allocated NASC -values were averaged for ICES-squares (0.5° latitude by 1° longitude). For each statistical square, the unit area density of fish (rA) in number per square nautical mile (N*nm-2) was calculated using standard equations (Foote et al., 1987; Toresen et al., 1998). To estimate the total abundance of fish, the unit area abundance for each statistical square was multiplied by the number of square nautical miles in each statistical square and then summed for all the statistical squares within defined subareas and over the total area. Biomass estimation was calculated by multiplying abundance in numbers by the average weight of the fish in each statistical square then summing all squares within defined subareas and over the total area. The Norwegian BEAM soft-ware (Totland and Godø 2001) was used to make estimates of total biomass.

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Acoustic estimates of herring and blue whiting abundance were obtained during the surveys using the Simrad ER60 scientific echosounder. The allocation of NASC-values to herring, blue whiting and other acoustic targets were based on the composition of the trawl catches and the appearance of echo recordings. To estimate the abundance, the allocated NASC -values were averaged for ICES-squares (0.5° latitude by 1° longitude). For each statistical square, the unit area density of fish (rA) in number per square nautical mile (N*nm-2) was calculated using standard equations (Foote et al., 1987; Toresen et al., 1998). To estimate the total abundance of fish, the unit area abundance for each statistical square was multiplied by the number of square nautical miles in each statistical square and then summed for all the statistical squares within defined subareas and over the total area. Biomass estimation was calculated by multiplying abundance in numbers by the average weight of the fish in each statistical square then summing all squares within defined subareas and over the total area. The Norwegian BEAM soft-ware (Totland and Godø 2001) was used to make estimates of total biomass.

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The development of the ecosystem approach and models for the management of ocean marine resources requires easy access to standard validated datasets of historical catch data for the main exploited species. They are used to measure the impact of biomass removal by fisheries and to evaluate the models skills, while the use of standard dataset facilitates models inter-comparison. North Atlantic albacore tuna is exploited all year round by longline and in summer and autumn by surface fisheries and fishery statistics compiled by the International Commission for the Conservation of Atlantic Tunas (ICCAT). Catch and effort with geographical coordinates at monthly spatial resolution of 1° or 5° squares were extracted for this species with a careful definition of fisheries and data screening. In total, thirteen fisheries were defined for the period 1956-2010, with fishing gears longline, troll, mid-water trawl and bait fishing. However, the spatialized catch effort data available in ICCAT database represent a fraction of the entire total catch. Length frequencies of catch were also extracted according to the definition of fisheries above for the period 1956-2010 with a quarterly temporal resolution and spatial resolutions varying from 1°x 1° to 10°x 20°. The resolution used to measure the fish also varies with size-bins of 1, 2 or 5 cm (Fork Length). The screening of data allowed detecting inconsistencies with a relatively large number of samples larger than 150 cm while all studies on the growth of albacore suggest that fish rarely grow up over 130 cm. Therefore, a threshold value of 130 cm has been arbitrarily fixed and all length frequency data above this value removed from the original data set.