865 resultados para Golden Gate International Exposition (1939-1940 : San Francisco, Calif.)


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El presente Trabajo de Grado busca caracterizar la cultura organizacional de una empresa del sector Financiero en Colombia y realizar orientaciones de acciones para el cambio organizacional de acuerdo con la estrategia de perdurabilidad establecida por la Alta Dirección de dicha empresa. Para este fin, se realiza una cuidadosa revisión y actualización del estado del arte de los conceptos clave ¨Cultura Organizacional¨ y ¨Cambio Organizacional¨. Es de resaltar que para el primero de ellos, se toma como punto de partida el estado del arte sobre Cultura Organizacional realizado por el profesor Carlos Eduardo Méndez Álvarez y cuyo marco temporal abarca desde los orígenes del concepto en el siglo XIX hasta el año 2006. Asimismo, luego de una cuidadosa revisión de los Modelos de Cambio Organizacional existentes y de la realidad de la empresa objeto de estudio, se adopta el Modelo ADKAR que consta de cinco fases: Conciencia del Cambio, Deseo, Conocimiento, Capacidad – Habilidad y Refuerzo. Asimismo, a partir de la construcción de un fundamento teórico sólido y a través de la aplicación de la metodología para describir la Cultura Organizacional en Colombia MEDECO se busca una aproximación a la Cultura Organizacional de la empresa objeto de estudio con el fin de describir e identificar los rasgos predominantes de su cultura organizacional y entregar una propuesta final con los rasgos necesarios que alientan la consecución exitosa de los procesos de cambio.

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Pós-graduação em Agronomia (Produção Vegetal) - FCAV

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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)

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Introduction 1.1 Occurrence of polycyclic aromatic hydrocarbons (PAH) in the environment Worldwide industrial and agricultural developments have released a large number of natural and synthetic hazardous compounds into the environment due to careless waste disposal, illegal waste dumping and accidental spills. As a result, there are numerous sites in the world that require cleanup of soils and groundwater. Polycyclic aromatic hydrocarbons (PAHs) are one of the major groups of these contaminants (Da Silva et al., 2003). PAHs constitute a diverse class of organic compounds consisting of two or more aromatic rings with various structural configurations (Prabhu and Phale, 2003). Being a derivative of benzene, PAHs are thermodynamically stable. In addition, these chemicals tend to adhere to particle surfaces, such as soils, because of their low water solubility and strong hydrophobicity, and this results in greater persistence under natural conditions. This persistence coupled with their potential carcinogenicity makes PAHs problematic environmental contaminants (Cerniglia, 1992; Sutherland, 1992). PAHs are widely found in high concentrations at many industrial sites, particularly those associated with petroleum, gas production and wood preserving industries (Wilson and Jones, 1993). 1.2 Remediation technologies Conventional techniques used for the remediation of soil polluted with organic contaminants include excavation of the contaminated soil and disposal to a landfill or capping - containment - of the contaminated areas of a site. These methods have some drawbacks. The first method simply moves the contamination elsewhere and may create significant risks in the excavation, handling and transport of hazardous material. Additionally, it is very difficult and increasingly expensive to find new landfill sites for the final disposal of the material. The cap and containment method is only an interim solution since the contamination remains on site, requiring monitoring and maintenance of the isolation barriers long into the future, with all the associated costs and potential liability. A better approach than these traditional methods is to completely destroy the pollutants, if possible, or transform them into harmless substances. Some technologies that have been used are high-temperature incineration and various types of chemical decomposition (for example, base-catalyzed dechlorination, UV oxidation). However, these methods have significant disadvantages, principally their technological complexity, high cost , and the lack of public acceptance. Bioremediation, on the contrast, is a promising option for the complete removal and destruction of contaminants. 1.3 Bioremediation of PAH contaminated soil & groundwater Bioremediation is the use of living organisms, primarily microorganisms, to degrade or detoxify hazardous wastes into harmless substances such as carbon dioxide, water and cell biomass Most PAHs are biodegradable unter natural conditions (Da Silva et al., 2003; Meysami and Baheri, 2003) and bioremediation for cleanup of PAH wastes has been extensively studied at both laboratory and commercial levels- It has been implemented at a number of contaminated sites, including the cleanup of the Exxon Valdez oil spill in Prince William Sound, Alaska in 1989, the Mega Borg spill off the Texas coast in 1990 and the Burgan Oil Field, Kuwait in 1994 (Purwaningsih, 2002). Different strategies for PAH bioremediation, such as in situ , ex situ or on site bioremediation were developed in recent years. In situ bioremediation is a technique that is applied to soil and groundwater at the site without removing the contaminated soil or groundwater, based on the provision of optimum conditions for microbiological contaminant breakdown.. Ex situ bioremediation of PAHs, on the other hand, is a technique applied to soil and groundwater which has been removed from the site via excavation (soil) or pumping (water). Hazardous contaminants are converted in controlled bioreactors into harmless compounds in an efficient manner. 1.4 Bioavailability of PAH in the subsurface Frequently, PAH contamination in the environment is occurs as contaminants that are sorbed onto soilparticles rather than in phase (NAPL, non aqueous phase liquids). It is known that the biodegradation rate of most PAHs sorbed onto soil is far lower than rates measured in solution cultures of microorganisms with pure solid pollutants (Alexander and Scow, 1989; Hamaker, 1972). It is generally believed that only that fraction of PAHs dissolved in the solution can be metabolized by microorganisms in soil. The amount of contaminant that can be readily taken up and degraded by microorganisms is defined as bioavailability (Bosma et al., 1997; Maier, 2000). Two phenomena have been suggested to cause the low bioavailability of PAHs in soil (Danielsson, 2000). The first one is strong adsorption of the contaminants to the soil constituents which then leads to very slow release rates of contaminants to the aqueous phase. Sorption is often well correlated with soil organic matter content (Means, 1980) and significantly reduces biodegradation (Manilal and Alexander, 1991). The second phenomenon is slow mass transfer of pollutants, such as pore diffusion in the soil aggregates or diffusion in the organic matter in the soil. The complex set of these physical, chemical and biological processes is schematically illustrated in Figure 1. As shown in Figure 1, biodegradation processes are taking place in the soil solution while diffusion processes occur in the narrow pores in and between soil aggregates (Danielsson, 2000). Seemingly contradictory studies can be found in the literature that indicate the rate and final extent of metabolism may be either lower or higher for sorbed PAHs by soil than those for pure PAHs (Van Loosdrecht et al., 1990). These contrasting results demonstrate that the bioavailability of organic contaminants sorbed onto soil is far from being well understood. Besides bioavailability, there are several other factors influencing the rate and extent of biodegradation of PAHs in soil including microbial population characteristics, physical and chemical properties of PAHs and environmental factors (temperature, moisture, pH, degree of contamination). Figure 1: Schematic diagram showing possible rate-limiting processes during bioremediation of hydrophobic organic contaminants in a contaminated soil-water system (not to scale) (Danielsson, 2000). 1.5 Increasing the bioavailability of PAH in soil Attempts to improve the biodegradation of PAHs in soil by increasing their bioavailability include the use of surfactants , solvents or solubility enhancers.. However, introduction of synthetic surfactant may result in the addition of one more pollutant. (Wang and Brusseau, 1993).A study conducted by Mulder et al. showed that the introduction of hydropropyl-ß-cyclodextrin (HPCD), a well-known PAH solubility enhancer, significantly increased the solubilization of PAHs although it did not improve the biodegradation rate of PAHs (Mulder et al., 1998), indicating that further research is required in order to develop a feasible and efficient remediation method. Enhancing the extent of PAHs mass transfer from the soil phase to the liquid might prove an efficient and environmentally low-risk alternative way of addressing the problem of slow PAH biodegradation in soil.

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24 Briefe zwischen Richard Bach und Max Horkheimer, 1938-1940; 2 Briefe zwischen Alfred Chalk und Max Horkheimer, 17.10.1939, 14.11.1939; 3 Briefe von Morduch Lexandrowitsch und der American Consulate General, 1939; 4 Briefe von der American Consulate General und Max Horkheimer, 1938-1939; 1 Brief von Max Horkheimer an das Amtstgericht Berlin, 15.03.1939; 1 Brief von Max Horkheimer an Stiedry, 05.12.1938; 1 Brief von Max Horkheimer an den Collector of Custom, 26.10.1938; 2 Briefe zwischen Josef Maier und Carson Alexandrowitsch, 28.06.1938, 29.06.1938; 1 Brief von Margarete Baruch an Alice Maier, 11.04.1938; 1 Brief von Emanuel List an Carson Alexandrowitsch, 23.02.1938; 1 Abschrift des Briefes von der Metropolitan Opera Association New York an Morduch Lexandrowitsch, 22.02.1938; 1 Brief von Jacques Barzun an Max Horkheimer, 09.07.1947; 4 Briefe zwischen K. Baschwitz und Max Horkheimer, 1938-1946; 2 Briefe zwischen E. Bauer und Max Horkheimer, 08.04.1935, 27.05.1935; 4 Briefe zwischen Fritz Bauer und Max Horkheimer, 1937-1938; 2 Briefe zwischen Lina Bauer und Max Horkheimer, 20.07.1942, 16,08,1942; 4 Briefe zwsichen Rudolf Bauer und Max Horkheimer, 1937; 15 Briefe zwischen Gertrud Bauer und Max Horkheimer, 1938-1941; 1 Brief von Max Horkheimer an den Collector of Customs, 15.03.1940; 2 Briefe zwischen I. Hannah Davidson vom Jewish Community Center San Francisco und Max Horkheimer, 19.09.1938, 29.09.1938; 2 Briefe zwsichen I. Bauer und Max Horkheimer, 25.09.1938, 29.09.1938; 1 Brief von Max Horkheimer an Klopfer, 27.09.1938; 3 Briefe zwischen Y.M.H.A. - Y.W.H.A The Jewish Center of Saint Louis und Max Horkheimer, 19.09.1938, 1938; 1 Brief von Max Horkheimer an Julius Rosenberg, 17.09.1938; 1 Brief von Max Horkheimer an das Jwish Center Salt Lake City, Utah, 07.09.1938; 1 Brief von Max Horkheimer an das Jewish Community Center San Fransisco, 07.09.1938; 3 Briefe zwischen dem New York Section of the National Council of Jewish Women und Max Horkheimer, 07.04.1938, 1938; 2 Briefe zwischen Baum und Max Horkheimer, 12.03.1946, 25.05.1946; 1 Brief von Max Horkheimer an Charles A. Beard , 12.12.1934; 1 Brief von Charles A. Beard an C. A. Beard; 5 Briefe von Friedrich Pollock an Charles A. Beard, 1940-1941; 5 Briefe zwischen Lilo Beck und Max Horkheimer, 1940-1941; 7 Briefe zwischen Maximilian Beck und Max Horkheimer, 1939-1940; 1 Brief von Paul Tillich an Max Horkheimer , 01.10.1940; 1 Brief von dem Emergency Committee in Aid of Displaced Foreign Scholars New York an Max Horkheimer, 19.04.1940; 5 Briefe zwischen Konrad Bekker und Max Horkheimer, 1936-1939; 2 Briefe von Max Horkheimer an Ludwig Bendix, 1921, 1937; 1 Brief von Peter Bendmann an Max Horkheimer; 1 Brief von Max Horkheimer an Ruth Benedict, 30.07.1937; 1 Brief von Eric Russel Bentley an Max Horkheimer, 30.01.1945; 1 Brief von George Berg an Max Horkheimer, 12.07.1945; 2 Briefe zwischen Egon Bergel und Max Horkheimer, 18.08.1938, 22.08.1938; 1 Brief von Marie Jahoda an Max Horkheimer, 14.07.1928; 1 Brief von Theodor W. Adorno an Kurt Bergel, 09.09.1939; 15 Briefe zwischen Klaus Berger und Max Horkheimer, 1936-1943; 1 Brief von Frederick Pollock an Philip M. Hayden von der Columbia University New York, 05.03.1942; 1 Brief von Hans Venedey an Max Horkheimer, 05.03.1938; 1 Brief von Max Horkheimer an Ida Berger-Chevant, 18.02.1939;

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1 Brief von Margot von Mendelssohn an Max Horkheimer, 20.05.1948; 6 Briefe zwsichen Charles E. Merriam und Max Horkheimer, 1940-1941; 4 Briefe zwischen Josef Messinger und Max Horkheimer, 1940; 1 Curriculum Vitae von Alfred Meusel an Max Horkheimer; 1 Brief von Max Horkheimer an Gerhard Meyer, 17.10.1938; 3 Briefe zwischen Hans A. Meyer und Max Horkheimer´09.10.1939, 1947; 2 Briefe zwischen Julie Meyer und Max Horkheimer, 12.04.1941, 15.04.1941; 43 Briefe zwischen Hermann Meyer-Lindenberg, Oscar Meyer und Max Horkheimer sowie Briefwechsel mit Hadley Cantril; 2 Briefe zwischen Hadley Cantril und Theodor W. Adorno, 22.05.1941, 28.05.1941; 1 Brief von Jerome Michael an Margot von Mendelssohn, 10.01.1941; 2 Briefe und 2 Beilagen zwischen Joseph Mire und Max Horkheimer, 16.03.1941, 28.03.1941; 6 Briefe zwischen Mitchell, Silberberg & Knupp, Los Angeles und Max Horkheimer, 1942, 1943; 1 Brief von Friedrich Pollock an Wesley C. Mitchell, 06.08.1940; 3 Briefe zwischen Hans Mohr und Max Horkheimer, 29.03.1946, 1946; 1 Brief von Herbert Moeller Morton an Max Horkheimer, 25.02.1940; 1 Brief von Max Horkheimer an den Chairman of the Committee on General Scholarships, Cambridge Massachusetts, 01.03.1940; 2 Briefe von David H. Moses an Max Horkheimer, 1939; 1 Brief von Franz Neumann an Philip Mosley, 28.04.1941; 49 Briefe zwischen Dorthy I. Mulgrave und Max Horkheimer, 1936-1940; 1 Brief von Max Horkheimer an das Municipal Court, San Francisco, 24.12.1948;

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58 Briefe zwischen Paul Massing und Max Horkheimer, 1940 - 1949; 15 Briefe zwischen Alice H. Maier und Paul Massing, 1950 - 1964; 4 Briefe zwischen Paul Massing und Fred M. Stein, 1943; 1 Brief an Marc Vosk von Paul Massing, 25.10.1949; 2 Briefe zwischen Paul Massing und James T. Shotwell, Juni 1947; 1 Brief von Max Horkheimer an das Chancellor Hotel (San Francisco), 08.01.1947; 2 Brief von dem American Friends Service Committee (Philadelphia) an Max Horkheimer, 1946/1947; 1 Brief an Leo Löwenthal von Paul Massing, 09.08.1949; 1 Brief an Paul Massing von Samuel J. Kramer, 15.01.1945; 44 Briefe zwischen Max Horkheimer und Heinz Maus, 1939 - 1950; 3 Briefe von Heinz Maus an Leo Löwenthal, 1948- 1949; 1 Brief von Margot von Mendelssohn an Max Horkheimer, 29.03.1948;

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Implantación de la Red de Alta velocidad Ferroviaria en California. Tramo Fresno-Sacramento. El presente articúlo es la cuarta parte de la serie "Alta Velocidad Ferroviaria en California (CHSRS)". Recoge la Alternativa "Stockton Arch", que el Proyecto FARWEST presenta a la prevista por la Authority (CHSRA), para la Línea HSR Fresno-Sacramento, en programación y en trazado. Éste discurre, desde la gran Terminal de Fresno (implantada en las afueras al suroeste de la ciudad) por el segmento sur del "mar interior" (que en el Terciario Superior ocupaba el actual Valle Central), hasta Stockton, y por el segmento norte, hasta Sacramento. El Paet de Ripperdan (~ pK 40) queda conectado por carretera con el PAET de Oroloma de la Línea HSR Fresno-San Francisco (Golden Gate Alternative). La última parte del trazado de la Línea HSR Fresno-Sacramento (Stockton Arch Alternative), coincide en alineación y rasante con la Línea HSR San Francisco-Sacramento (Crossing Bay Alternative) a la altura de Roseville, donde se emplaza la gran terminal norte de la red de California, desde la que se unirá ésta con la de Nevada, por Reno. This article forras the fourth part of the series entitled "High Speed Railway in California (CHSRS)". It addresses the "Stockton Arch" alternative, which the FARWESTProjectpresents in scheduling and in alignment as to that provided for by the Authority (CHSRA) for the Fresno-Sacramento HSR Line. The latter runs from the grand Fresno Terminal (located in the outskirts to the southwest ofthe city) through the south segment ofthe "inland sea" (which oceupied the current Central Valley in the Upper Tertiary) to Stockton and through the north segment to Sacramento. The Ripperdan TSAP (post ofpassing and stabling trains), — kilometer point 40, conneets with the Oroloma TSAP ofthe Fresno-San Francisco HSR Line (Golden Gate Alternative) by road. The last part of the Fresno-Sacramento HSR Line alignment (Stockton Arch Alternative), coincides in alignment and grade with the San Francisco-Sacramento HSR Line (Crossing Bay Alternative) at Roseville, where the great north terminal ofthe California network is located, from which the latter will be linked with Nevada s network through Reno.

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Cover title.

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"Biennial statistical report to the Legislature."

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"Granted a medal of award by the Panama-Pacific international exposition, San Francisco, California, 1915."