El GATT 94 y la Organización Mundial del Comercio: una nueva agenda para Uruguay

Incluye Bibliografía

Notas de Población Vol. 38 N° 94

En este número de la Revista Notas de Población se reúnen ocho trabajos sobre distintos temas relevantes en la investigación sociodemográfica en América Latina y el Caribe, que abarcan tanto escalas regionales como nacionales. En ellos se adoptan enfoques y metodologías orientadas a poner de relieve las transformaciones que acontecen en la población, sus espacios y ambientes, las familias y generaciones.

Aspectos ecológicos do bacu-pedra Lithodoras dorsalis (Valenciennes, 1840) (Siluriformes: Doradidae) na foz amazônica, Brasil

O objetivo deste estudo foi investigar aspectos alimentares do bacu-pedra Lithodoras dorsalis (Siluriformes: Doradidae) na região da foz Amazônica e seu possível papel como dispersor de sementes. As coletas dos espécimes de L. dorsalis foram realizadas mensalmente de julho de 2010 a junho de 2011, totalizando 371 espécimes capturados. Por meio da análise das gônadas constatou-se que todos os espécimes coletados encontravam-se imaturos, caracterizando-os como jovens. O comprimento padrão médio foi igual a 15,40cm (DP ± 4,87cm) e a massa total média igual a 94g (DP ± 149,45g). A dieta da espécie foi composta por 28 itens alimentares, dos quais 16 foram de origem alóctone e 12 de origem autóctone, o que define a espécie como herbívora, com forte tendência à frugivoria devido aos altos valores de importância de frutos e sementes presente em sua dieta. Houve diferença entre os períodos pluviométricos com relação a sazonalidade alimentar, sendo o final do período de transição entre chuva estiagem e o início da estiagem os períodos de menor e maior atividade alimentar, respectivamente. Porém, a importância dos itens consumidos entre os períodos pluviométricos não apresentou diferença, sendo que a dieta da espécie foi similar durante todo o período de coleta. Quanto à ictiocoria, dos 371 espécimes de Lithodoras dorsalis coligidos, 268 (74,93%) apresentaram frutos e sementes em seus estômagos (principalmente açaí Euterpe oleracea Mart., aninga Montrichardia linifera (Arruda) Schott e buriti Mauritia flexuosa Mart). Para as análises de germinação foram utilizadas sementes do açaí Euterpe oleracea Mart. e da aninga Montrichardia linifera (Arruda) Schott por atingirem quantidade suficiente de amostras. A partir da análise do trato digestivo do bacu-pedra constatou-se que todas as sementes de Euterpe oleracea Mart. apresentavam-se intactas, havendo um aumento no desempenho germinativo, porém o mesmo não ocorreu para as estruturas germinativas de aninga Montrichardia linifera (Arruda) Schott, algumas das quais apresentaram-se destruídas devido ao processo digestivo. Concluiu-se que Lithodoras dorsalis é um potencial dispersor do açaí Euterpe oleracea Mart. na Foz Amazônica, uma vez que há um aumento do desempenho germinativo das sementes. Foi constatado um acréscimo na quantidade de frutos e sementes consumidos à medida que os indivíduos aumentam o tamanho corporal. Por fim, tendo em vista o alto consumo de material de origem alóctone por Lithodoras dorsalis, destaca-se a importância da vegetação ripária por fornecer itens como frutos essenciais na dieta desta e de outras espécies de peixes neotropicais. Além disso, Lithodoras dorsalis parece fazer parte do mecanismo de algumas espécies de plantas para a colonização de novas áreas (ictiocoria), como no caso do açaí Euterpe oleracea Mart.

Frequências de alimentação sobre o comportamento ingestivo, digestibilidade do amido e flutuação de consumo em bovinos Nelore confinados

Pós-graduação em Ciência e Tecnologia Animal - FEIS

Efeito das frequências de alimentação sobre o desempenho, características de carcaça e saúde ruminal de bovinos nelore confinados

Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

Da letargia ao realento: notas sobre o ensino de graduação em administração pública no Brasil no entremeio da crise do Estado e da redemocratização no país (1983-94)

Considering the meantime of Brazilian crisis of State and redemocratization, this article looks for a description and analysis of the facts and circumstances that marked the undergraduate education of Brazilian public administration during this period, considered by the authors as one of the cycles (or stages of construction) of academic education. Methodologically, this article makes a review of academic and non-academic works which deal directly and indirectly the PA themes, including revisiting the sources and analyzing the existing laws and opinions about the undergraduate education in public administration in a continuum of time between 1983-94, through a semi-structured interview with academics who have experienced such period. Regarding the results, this article observes that the period between 1983-94, unlike the first cycle (1952-65) and second cycle (1966-82), when the academic background in public administration had an identity - adherent to the conception (and project) of State and the contours (and production) in the public administration field of knowledge - having the Ebap/FGV a model case, was a problematic stage of construction, reflecting the crisis of State in the 80's years and also the paradigmatic crisis (or discontinuity) in public administration field of knowledge in Brazil during this time.

Cediranib Plus FOLFOX/CAPOX Versus Placebo Plus FOLFOX/CAPOX in Patients With Previously Untreated Metastatic Colorectal Cancer: A Randomized, Double-Blind, Phase III Study (HORIZON II)

Purpose Cediranib is a highly potent inhibitor of vascular endothelial growth factor (VEGF) signaling with activity against all three VEGF receptors. HORIZON II [Cediranib (AZD2171, RECENTIN) in Addition to Chemotherapy Versus Placebo Plus Chemotherapy in Patients With Untreated Metastatic Colorectal Cancer] assessed infusional fluorouracil, leucovorin, and oxaliplatin/capecitabine and oxaliplatin (FOLFOX/CAPOX) with or without cediranib in patients with previously untreated metastatic colorectal cancer (mCRC). Patients and Methods Eligible patients were initially randomly assigned 1:1:1 to receive cediranib (20 or 30 mg per day) or placebo plus FOLFOX/CAPOX. In an early analysis of this and two other cediranib studies (HORIZON I [Cediranib Plus FOLFOX6 Versus Bevacizumab Plus FOLFOX6 in Patients With Previously Treated Metastatic Colorectal Cancer] and HORIZON III [Cediranib Plus FOLFOX6 Versus Bevacizumab Plus FOLFOX6 in Patients With Untreated Metastatic Colorectal Cancer]), the 20-mg dose met the predefined criteria for continuation. Subsequent patients were randomly assigned 2: 1 to the cediranib 20 mg or placebo arms. Progression-free survival (PFS) and overall survival (OS) were coprimary end points. Results In all, 860 patients received cediranib 20 mg (n = 502) or placebo (n = 358). The addition of cediranib to FOLFOX/CAPOX resulted in PFS prolongation (hazard ratio [HR], 0.84; 95% CI, 0.73 to 0.98; P = .0121; median PFS, 8.6 months for cediranib v 8.3 months for placebo) but had no impact on OS (HR, 0.94; 95% CI, 0.79 to 1.12; P = .5707; median OS, 19.7 months for cediranib v 18.9 months for placebo). There were no significant differences in the secondary end points of objective response rate, duration of response, or liver resection rate. Median chemotherapy dose-intensity was decreased by approximately 10% in patients treated with cediranib. Adverse events (AEs) associated with cediranib were manageable. Conclusion Addition of cediranib 20 mg to FOLFOX/CAPOX resulted in a modest PFS prolongation, but no significant difference in OS. The cediranib AE profile was consistent with those from previous studies. Because of the lack of improvement in OS, cediranib plus an oxaliplatin-based regimen cannot be recommended as a treatment for patients with mCRC. J Clin Oncol 30:3596-3603. (C) 2012 by American Society of Clinical Oncology

Bioremediation of PAHs - Limitations and soultions

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.