Efeitos de Z' nos modelos left-right, B-L e 331

Pós-graduação em Física - IFT

Frances Anderson Gilmer Papers - Accession 247 - M104 (133-134)

The Frances Anderson Gilmer Papers consists of electrostatic photocopies of the following: genealogical records; biographical sketches; Records relating to the Sons of the American Revolution (SAR) and Daughters of the American Revolution (DAR); copy of the “The Revolutionary Soldiers of Catholic Presbyterian Church of Chester County, South Carolina" by Mary Wylie Strange; Diary of S. T. Anderson: Confederate Prisoner of War 1864-1865 by Margaret Anderson Harden (1908). Lt. Samuel Thompson of Anderson (1838-1894) was a Confederate soldier during the American Civil War in Co. D 1st South Carolina Cavalry. The genealogical records relate to the following families: Anderson, Wylie. McCalla, McKown, Yeamans, Moore (i.e., Governor James Moore) and Adair.

EC31-133 The Management of Nebraska Soils (Revised March 1936)

The agricultural lands of this country are its greatest natural resource. History points out that nations with vast areas of good farm land are most likely to prosper and survive over long periods of time. Local communities, too, prosper and flourish in proportion to the productiveness of the surrounding land. Schools, social life, and business develop best in areas where the land is productive and properly managed and conserved. Nebraska, in common with other states, has suffered by the depletion of soil fertility. The reduction in acres in legumes and grasses, and the deplation of the organic matter in the surface soils, has likewise had its effect on the run-off of precipitation, soil blowing, and damage from drouth. In order to know what elements of fertility may become deficient and how soil fertility may be restored and maintained, we should understand the composition, character, and management of soils. In the following pages, some fundamentals of soil feritlity are given, followed later by a discussion of practical soil-management practices.

The young stellar cluster [DBS2003] 157 associated with the H ii region GAL 331.31-00.34

We report a study of the stellar content of the near-infrared (NIR) cluster [DBS2003] 157 embedded in the extended H ii region GAL 331.31-00.34, which is associated with the IRAS source 16085-5138. JHK photometry was carried out in order to identify potential ionizing candidates, and the follow-up NIR spectroscopy allowed the spectral classification of some sources, including two O-type stars. A combination of NIR photometry and spectroscopy data was used to obtain the distance of these two stars, with the method of spectroscopic parallax: IRS 298 (O6 V, 3.35 +/- 0.61 kpc) and IRS 339 (O9 V, 3.24 +/- 0.56 kpc). Adopting the average distance of 3.29 +/- 0.58 kpc and comparing the Lyman continuum luminosity of these stars with that required to account for the radio continuum flux of the H ii region, we conclude that these two stars are the ionizing sources of GAL 331.31-00.34. Young stellar objects (YSOs) were searched by using our NIR photometry and mid-infrared (MIR) data from the Galactic Legacy Infrared Mid-Plane Survey Extraordinaire (GLIMPSE) survey. The analysis of NIR and MIR colourcolour diagrams resulted in 47 YSO candidates. The GLIMPSE counterpart of IRAS 16085-5138, which presents IRAS colour indices compatible with an ultracompact H ii region, has been identified. The analysis of its spectral energy distribution between 2 and m revealed that this source shows a spectral index a= 3.6 between 2 and m, which is typical of a YSO immersed in a protostellar envelope. Lower limits to the bolometric luminosity and the mass of the embedded protostar have been estimated as L= 7.7 x 10(3) L? and M= 10 M?, respectively, which correspond to a B0B1 V zero-age main sequence star.

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.

Studio di fase I sulla reinfusione intraepatica di cellule staminali CD 133+ altamente purificate nei pazienti con malattia epatica terminale

Numerose evidenze sperimentali hanno dimostrato il contributo delle cellule staminali di derivazione midollare nei processi di rigenerazione epatica dopo danno tissutale. E’ cresciuto pertanto l’interesse sul loro potenziale impiego in pazienti con cirrosi. Questo studio si propone di valutare la fattibilità e la sicurezza della reinfusione intraepatica di cellule staminali midollari autologhe CD133+ in 12 pazienti con insufficienza epatica terminale definita da un punteggio di Model for End Stage of Liver Disease (MELD) compreso tra 17 e 25. L’efficacia in termini di funzionalità epatica rappresenta un obiettivo secondario. Previa mobilizzazione nel sangue periferico mediante somministrazione di granulocyte-colony stimulating factor (G-CSF) alla dose di 7,5 mcg/Kg/b.i.d. e raccolta per leucoaferesi, le cellule CD133+ altamente purificate vengono reinfuse in arteria epatica a partire da 5x104/Kg fino a 1x106/kg. Nei tre giorni successivi si somministra G-CSF per favorire l’espansione e l’attecchimento delle cellule. Durante la mobilizzazione, la reinfusione e nei 12 mesi successivi i pazienti sono sottoposti a periodici controlli clinici, laboratoristici e strumentali e ad attenta valutazione di effetti collaterali. Lo studio è tuttora in corso e ad oggi, 11 pazienti sono stati sottoposti a reinfusione e 4 hanno completato i 12 mesi di follow-up. Il G-CSF è stato ben tollerato e ha consentito di ottenere una buona espansione cellulare. Dopo la reinfusione sono stati documentati un ematoma inguinale e due episodi transitori di encefalopatia portosistemica. Durante il follow-up 4 pazienti sono stati trapiantati e 2 sono morti. Non è stata osservata alcuna modificazione significativa degli indici di funzione epatica. Questi risultati preliminari confermano la possibilità di mobilizzare e reinfondere un numero adeguato di cellule staminali di derivazione midollare in pazienti con malattia epatica in stadio terminale.

I profili fiscali delle operazioni di riorganizzazione societaria transfrontaliere nell'Unione Europea: Il regime fiscale comune della direttiva 2009/133/CE e le prospettive di sviluppo normativo

La tesi affronta le problematiche fiscali della riorganizzazione societaria e la soluzione adoperata nell’Unione europea per le operazioni di carattere transfrontaliere. Si parte dalla definizione del termine “riorganizzazione societaria”, evidenziando le sue matici economiche e la varietà del suo contenuto secondo l’ordinamento giuridico e la branca del diritto di riferimento. Si prosegue sulla correlazione fra l’ampliazione del contenuto della libertà di stabilimento, dovuta maggiormente all’attività interpretativa della Corte di giustizia, e l’allargamento del concetto di riorganizzazione societaria nel quadro normativo dell’Unione. Si procede dunque all’analisi del regime fiscale comune della direttiva 2009/133/CE intravedendosi i suoi sviluppi successivi. In sede di conclusioni, si apporta un breve riassunto sullo stato della questione in Brasile e si riflette sull’attendibilità del modello impositivo dell’Unione quale parametro per una futura riforma fiscale in Brasile.

Grauzonen : Funktionsweisen der Beniner Polizei und ihr Verhältnis zur Bevölkerung /// Arbeitspapiere / Institut für Ethnologie und Afrikastudien ; 133

Gewalttätig, korrupt und faul oder eher gesetzestreu, hilfsbereit und freundlich? Diese Abhandlung befasst sich mit der Arbeitsweise der Beniner Polizei und den Bildern, die sie von sich erzeugt und den Eindrücken, die sie bei den Bürgern hinterlässt. Die Arbeit liefert Erkenntnisse über den Aufbau und die Arbeitsweise der Beniner Polizei. Sie verweist auch auf das Konkurrenzverhältnis der Polizei zu anderen Sicherheitskräften, wie etwa der Gendarmerie und sie zeigt, dass sich die Polizeirnin diversen Grauzonen – der Legalität, der Staatlichkeit und der Formalität – bewegt. Informelle Strategien, schleichende Privatisierung und Korruption sichern in einem gewissen Rahmen das Funktionieren der Institution. Diese Schwächen der Institution haben jedoch negative Auswirkungen auf das Bild der Polizei und ihr Verhältnis zu den Bürgern. Nicht das propagierte Ideal einer Polizei, sondern die realen Interaktionen mit ihr dominieren die Wahrnehmung der Bürger von der Organisation.