937 resultados para James Clements Municipal Airport
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Many airports around the world are diversifying their land use strategies to integrate non-aeronautical development. These airports embrace the “airport city” concept to develop a wide range of commercial and light industrial land uses to support airport revenues. The consequences of this changing urban form are profound for both airport and municipal planners alike and present numerous challenges with regard to integration of airport and regional planning. While several tools exist for regional planning and airport operational planning, no holistic airport landside and regional planning tool exist. What is required is a planning support system that can integrate the sometimes conflicting stakeholder interests into one common goal for the airport and the surrounding region. This paper presents a planning support system and evaluates its application to a case study involving Brisbane Airport and the South East Queensland region in Australia.
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Ao longo da história, poucos fenômenos despertaram tanto interesse dos cidadãos, dispenderam tantos recursos do Estado e contribuíram tanto para o atraso de seu desenvolvimento quanto o problema da corrupção dos agentes públicos. Nesta tese, uso o conceito de improbidade para definir um tipo particular de fenômeno e distingui-lo de outros geralmente abrangidos pelo conceito de corrupção. A partir daí procuro responder as seguintes questões: quais elementos influenciam o processo de tomada de decisão do agente público para que considere o engajamento em uma improbidade? Que fatores estão associados à ocorrência de improbidades na Administração Pública municipal brasileira? Sob a perspectiva da nova economia institucional, a primeira parte da tese procede com a análise conceitual e metodológica do fenômeno, consubstanciado no referencial analíticos das improbidades, sustentando que: a) as improbidades correspondem a um gênero de atitudes oportunistas, dentre as quais se destaca uma espécie denominada transação corrupta; b) o processo de tomada de decisão do agente público, inserido no contexto de racionalidade limitada, orienta-se igualmente por elementos da análise custo-benefício (maximização da utilidade esperada), da dinâmica dos processos de aprendizagem e da barreira ético-moral dos próprios indivíduos. As demais partes da tese apresentam os resultados de uma investigação empírica sistemática, baseada nas informações de uma amostra aleatória de 960 municípios brasileiros auditados pela Controladoria-Geral da União. A análise evidencia os fatores associados à ocorrência das improbidades, tanto sob o ponto vista da literatura tradicional (modernização, capital social e rent-seeking), quanto da nova perspectiva analítica proposta, baseada nos mecanismos de governança. O teste a partir dos modelos tradicionais da literatura demonstra: a) a associação negativa entre a ocorrência das improbidades e os indicadores de desempenho institucional e de desenvolvimento socioeconômico dos municípios (em consonância com os efeitos comumente atribuídos as improbidades); b) a associação negativa entre a ocorrência das improbidades e os indicadores de modernização e de capital social dos municípios (em consonância com as causas comumente atribuídas as improbidades); c) a não associação entre a ocorrência das improbidades nos municípios brasileiros e os indicadores de incentivo ao comportamento rent-seeking (em oposição à clássica proposição de que quanto maior o tamanho do Estado, maior será a ocorrência de improbidades em razão dos incentivos oriundos de seu monopólio). Com base nos resultados obtidos, incorporo os supostos neoinstitucionalistas a análise das improbidades, interpretando-os como decorrência da inadequação das estruturas de governança dos contratos. Assim, para além do impacto do arranjo institucional, que abarca o controle parlamentar, administrativo e jurisdicional interno e externo dos recursos públicos federais transferidos aos municípios, apresento evidências de que as variações observadas na contagem de improbidades nos municípios brasileiros estão diretamente relacionadas à qualidade de seus mecanismos de governança. Dentre esses, destacam-se aqueles de natureza democrática: os mecanismos de controle social (os conselhos municipais de políticas públicas); os mecanismos de promoção da transparência (a qualidade do governo eletrônico); e os mecanismos de accountability (a disputa político-eleitoral). De acordo com o referencial analítico das improbidades, a existência e operação desses mecanismos elevam os custos de transação do agente público que, mesmo superando as limitações da barreira ético-moral e de aprendizado, ainda considera um eventual engajamento nesse gênero de atitudes oportunistas.
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In 1874, Merritton, Ont. was incorporated a village with W.W. Waite as the first reeve. On July 1, 1918, the village was incorporated a town. The first mayor was Thomas F. Hastings. In 1961, Merritton, Grantham and Port Dalhousie amalgamated with St. Catharines, despite the opposition of the town councils and citizens.
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La globalización y la competitividad como realidad de las empresas, implica que los gerentes preparen a sus empresas de la mejor manera para sobrevivir en este mundo tan inestable y cambiante. El primer paso consta de investigar y medir como se encuentra la empresa en cada uno de sus componentes, tales como recurso humano, mercadeo, logística, operación y por último y más importante las finanzas. El conocimiento de salud financiera y de los riesgos asociados a la actividad de las empresas, les permitirá a los gerentes tomar las decisiones correctas para ser rentables y perdurables en el mundo de los negocios inmerso en la globalización y competitividad. Esta apreciación es pertinente en Avianca S.A. esto teniendo en cuenta su progreso y evolución desde su primer vuelo el 5 de diciembre de 1919 comercial, hasta hoy cuando cotiza en la bolsa de Nueva York. Se realizó un análisis de tipo descriptivo, acompañado de la aplicación de ratios y nomenclaturas, dando lugar a establecer la salud financiera y los riesgos, no solo de Avianca sino también del sector aeronáutico. Como resultado se obtuvo que el sector aeronáutico sea financieramente saludable en el corto plazo, pero en el largo plazo su salud financiera se ve comprometida por los riegos asociados al sector y a la actividad desarrollada.
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Includes bibliography
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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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Mode of access: Internet.
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"DOE/EV-0115."
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"DOE/EV-0116."
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Mode of access: Internet.
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Mode of access: Internet.
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Final report, issued Mar. 1978.
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Includes index.
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Cover title.