La temprana recepción de Émile Durkheim en la sociología argentina : Apropiaciones y reelaboraciones en los escritos de Leopoldo Maupas

El presente trabajo aborda la temprana recepción de la obra de uno de los clásicos de la Sociología, Emile Durkheim, en el ámbito local. En una primera instancia, se realiza un recorrido sobre las menciones que de la obra del sociólogo alsaciano se realizaron durante la primera etapa institucional de la disciplina sociológica en la Argentina (1898-1921), para luego avanzar, con especial énfasis, en la apropiación que Leopoldo Maupas, principal receptor de la teoría durkheimniana en el país en tanto mantuvo un diálogo directo con el sociólogo francés, realizara de la obra metodológica más importante de éste: Las reglas del método sociológico. Para este fin, se realiza una reconstrucción del debate mantenido entre éstos dos autores respecto de la posibilidad de la objetividad en el estudio de los fenómenos sociales. Para finalizar, se estudia la utilización, por parte del sociólogo argentino, de un conjunto de conceptos y categorías de cuño durkheimiano para el análisis de la realidad social argentina de la época en consideración

Durkheim en la Argentina : Sus primeros lectores y el debate con Leopoldo Maupas

El presente trabajo reconstruye la introducción de las ideas de un clásico de la sociología, Emile Durkheim, en el ámbito local. La preocupación central es la de reedificar los procesos de recepción de éste autor en el campo sociológico argentino durante su primera etapa institucional entre 1898-1921. La Introducción comienza con una reflexión sobre las posibilidades de apropiación de la obra de Durkheim por parte de los sociólogos vernáculos a la luz de la teoría de la recepción, teniendo en cuenta las dificultades de la recuperación de la historia de la disciplina en el país previa a 1957. El primer capítulo trata las ideas fundamentales del pensamiento comteano y, a partir de la influencia de las mismas en el sociólogo alsaciano, la formulación del método sociológico establecida por éste último. Este desarrollo teórico tiene por fin el explicitar la concepción de Durkheim del "hecho social", tópico que será objeto de debate con el sociólogo argentino Leopoldo Maupas. El segundo capítulo ofrece un contexto histórico y político del desarrollo de la obra de Durkheim. Se plantea que este autor accedió a cargos en la universidad a partir de la naturaleza laica y republicana de su teoría y de sus contactos políticos. A su vez, se consideran las condiciones políticas, culturales y sociales locales para la fundación de las primeras cátedras de sociología. El tercer capítulo da cuenta de las primeras menciones de Durkheim en Argentina y, centralmente, el debate generado a partir del intercambio epistolar que Maupas tuviera con él. Las conclusiones, finalmente, se desprenden de lo que se ha desarrollado en las páginas previas

Spatially explicit estimates of length and biomass of Micromesistius poutassou (Blue Whiting) and Clupea harengus (Norwegian spring spawning herring) from acoustic and trawl surveys in the North-East Atlantic (2004-2012)

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.

Spatially explicit estimates of length and biomass of Micromesistius poutassou (Blue Whiting) from acoustic and trawl surveys in the North-East Atlantic in May 2007

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.

Spatially explicit estimates of length and biomass of Micromesistius poutassou (Blue Whiting) from acoustic and trawl surveys in the North-East Atlantic in May 2005

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.

Compilation of Thunnus thynnus (bluefin tuna) catches in the Northeast Atlantic Ocean 1950-2010

The data have been extracted and compiled from various sources but mainly from the ICES data base. The ICES data are from catch databases downloaded from the ICES website on 2014-01-14. These data are resolved by ICES area, country and year. During inspection of these data, it was noted that Norwegian data for years before 1950 had not been entered into the catch database on the ICES website. ICES has been notified of this omission by B. R. MacKenzie. The Norwegian data from ICES Bulletins. Statistiques has been added. Additional historical bluefin tuna catch data from other fishery reports and sources have been included in the data file for years preceding those when countries started reported their landings officially to ICES. These additional data have been reported in the literature previously (MacKenzie and Myers 2007, Fisheries Research).

Durkheim en la Argentina : Sus primeros lectores y el debate con Leopoldo Maupas

El presente trabajo reconstruye la introducción de las ideas de un clásico de la sociología, Emile Durkheim, en el ámbito local. La preocupación central es la de reedificar los procesos de recepción de éste autor en el campo sociológico argentino durante su primera etapa institucional entre 1898-1921. La Introducción comienza con una reflexión sobre las posibilidades de apropiación de la obra de Durkheim por parte de los sociólogos vernáculos a la luz de la teoría de la recepción, teniendo en cuenta las dificultades de la recuperación de la historia de la disciplina en el país previa a 1957. El primer capítulo trata las ideas fundamentales del pensamiento comteano y, a partir de la influencia de las mismas en el sociólogo alsaciano, la formulación del método sociológico establecida por éste último. Este desarrollo teórico tiene por fin el explicitar la concepción de Durkheim del "hecho social", tópico que será objeto de debate con el sociólogo argentino Leopoldo Maupas. El segundo capítulo ofrece un contexto histórico y político del desarrollo de la obra de Durkheim. Se plantea que este autor accedió a cargos en la universidad a partir de la naturaleza laica y republicana de su teoría y de sus contactos políticos. A su vez, se consideran las condiciones políticas, culturales y sociales locales para la fundación de las primeras cátedras de sociología. El tercer capítulo da cuenta de las primeras menciones de Durkheim en Argentina y, centralmente, el debate generado a partir del intercambio epistolar que Maupas tuviera con él. Las conclusiones, finalmente, se desprenden de lo que se ha desarrollado en las páginas previas

Spatially explicit estimates of length and biomass of Micromesistius poutassou (Blue Whiting) from acoustic and trawl surveys in the North-East Atlantic in May 2008

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.

Educación estético-literaria : la poesía en la formación de lectores

Fil: Mathieu, María Carolina. Universidad Nacional de La Plata. Facultad de Humanidades y Ciencias de la Educación; Argentina.

Spatially explicit estimates of length and biomass of Clupea harengus (Norwegian spring spawning herring) from acoustic and trawl surveys in the North-East Atlantic in May 2005

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.

Spatially explicit estimates of length and biomass of Micromesistius poutassou (Blue Whiting) from acoustic and trawl surveys in the North-East Atlantic in May 2006

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.

Spatially explicit estimates of length and biomass of Clupea harengus (Norwegian spring spawning herring) from acoustic and trawl surveys in the North-East Atlantic in May 2006

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.

Spatially explicit estimates of length and biomass of Micromesistius poutassou (Blue Whiting) from acoustic and trawl surveys in the North-East Atlantic in May 2011

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.