917 resultados para Lambert, David M.: Speciation and recognition concept.Theory and application
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Background: Natural polyploidy has played an important role during the speciation and evolution of vertebrates, including anurans, with more than 55 described cases. The species of the Phyllomedusa burmeisteri group are mostly characterized by having 26 chromosomes, but a karyotype with 52 chromosomes was described in P. tetraploidea. This species was found in sintopy with P. distincta in two localities of São Paulo State (Brazil), where triploid animals also occur, as consequence of natural hybridisation. We analyse the chromosomes of P. distincta, P. tetraploidea, and their triploid hybrids, to enlighten the origin of polyploidy and to obtain some evidence on diploidisation of tetraploid karyotype.Results: Phyllomedusa distincta was 2n = 2x = 26, whereas P. tetraploidea was 2n = 4x = 52, and the hybrid individuals was 2n = 3x = 39. In meiotic phases, bivalents were observed in the diploid males, whereas both bivalents and tetravalents were observed in the tetraploid males. Univalents, bivalents or trivalents; metaphase II cells carrying variable number of chromosomes; and spermatids were detected in the testis preparations of the triploid males, indicating that the triploids were not completely sterile. In natural and experimental conditions, the triploids cross with the parental species, producing abnormal egg clutches and tadpoles with malformations. The embryos and tadpoles exhibited intraindividual karyotype variability and all of the metaphases contained abnormal constitutions. Multiple NORs, detected by Ag-impregnation and FISH with an rDNA probe, were observed on chromosome 1 in the three karyotypic forms; and, additionally, on chromosome 9 in the diploids, mostly on chromosome 8 in the tetraploids, and on both chromosome 8 and 9 in the triploids. Nevertheless, NOR-bearing chromosome 9 was detected in the tetraploids, and chromosome 9 carried active or inactive NORs in the triploids. C-banding, base-specific fluorochrome stainings with CMA3 and DAPI, FISH with a telomeric probe, and BrdU incorporation in DNA showed nearly equivalent patterns in the karyotypes of P. distincta, P. tetraploidea, and the triploid hybrids.Conclusions: All the used cytogenetic techniques have provided strong evidence that the process of diploidisation, an essential step for stabilising the selective advantages produced by polyploidisation, is under way in distinct quartets of the tetraploid karyotype. © 2013 Gruber et al.; licensee BioMed Central Ltd.
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Includes bibliography
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Includes bibliography
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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)
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O objetivo desta pesquisa é a construção e a aplicação de uma organização didática para a Geometria Analítica Plana, a partir do estudo dos Vetores, no 3º ano do ensino médio, à luz da Teoria Antropológica do Didático de Yves Chevallard e da teoria da Aprendizagem Significativa de David Ausubel. A pesquisa é de natureza qualitativa do tipo etnográfica na educação, de acordo com Marli André, e foi desenvolvido com um grupo de alunos em um contexto específico que é a preparação para o vestibular. A manipulação de objetos ostensivos para compreensão dos objetos não-ostensivos da Matemática serviu de categorias para análise das praxeologias vivenciadas em sala de aula. Concluímos que os alunos ao manipular as representações de objetos ostensivos resgatam conhecimentos matemáticos de forma articulada e integrada para a ancoragem de novos conhecimentos matemáticos. Observou-se também que a organização didática permite “economia de tempo”, no que diz respeito ao estudo destes conteúdos nesta etapa da vida escolar.
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Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES)
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The law that justifies the inclusion of people with disability in schools and companies has been in force since the end of the 1980thies. In view of its coercion, people with disabilities have been enrolled at schools and been employed in companies. This research attempts to analyze the inclusion process according to Axel Honneth's Social Recognition Theory. Backed by his three dimension recognition process, we show firstly that inclusion signifies a process of individuation and social inclusion. Then, we study the law in force, its goals and strategies of achievement. We show that recognition's approach allows interpreting the law of inclusion more generously - in a less positivistic way. Finally, we approach the conditions for schools and companies to accomplish the law of inclusion so conceived.
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Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)
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Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq)
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Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)
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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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Mining and processing of metal ores are important causes of soil and groundwater contamination in many regions worldwide. Metal contaminations are a serious risk for the environment and human health. The assessment of metal contaminations in the soil is therefore an important task. A common approach to assess the environmental risk emanating from inorganic contaminations to soil and groundwater is the use of batch or column leaching tests. In this regard, the suitability of leaching tests is a controversial issue. In the first part of this work the applicability and comparability of common leaching tests in the scope of groundwater risk assessment of inorganic contamination is reviewed and critically discussed. Soil water sampling methods (the suction cup method and centrifugation) are addressed as an alternative to leaching tests. Reasons for limitations of the comparability of leaching test results are exposed and recommendations are given for the expedient application of leaching tests for groundwater risk assessment. Leaching tests are usually carried out in open contact with the atmosphere disregarding possible changes of redox conditions. This can affect the original metal speciation and distribution, particularly when anoxic samples are investigated. The influence of sample storage on leaching test results of sulfide bearing anoxic material from a former flotation dump is investigated in a long-term study. Since the oxidation of the sulfide-bearing samples leads to a significant overestimation of metal release, a feasible modification for the conduction of common leaching tests for anoxic material is proposed, where oxidation is prevented efficiently. A comparison of leaching test results to soil water analyzes have shown that the modified saturation soil extraction (SSE) is found to be the only of the tested leaching procedures, which can be recommended for the assessment of current soil water concentrations at anoxic sites if direct investigation of the soil water is impossible due to technical reasons. The vertical distribution and speciation of Zn and Pb in the flotation residues as well as metal concentrations in soil water and plants were investigated to evaluate the environmental risk arising from this site due to the release of metals. The variations in pH and inorganic C content show an acidification of the topsoil with pH values down to 5.5 in the soil and a soil water pH of 6 in 1 m depth. This is due to the oxidation of sulfides and depletion in carbonates. In the anoxic subsoil pH conditions are still neutral and soil water collected with suction cups is in equilibrium with carbonate minerals. Results from extended x-ray absorption fine-structure (EXAFS) spectroscopy confirm that Zn is mainly bound in sphalerite in the subsoil and weathering reactions lead to a redistribution of Zn in the topsoil. A loss of 35% Zn and S from the topsoil compared to the parent material with 10 g/kg Zn has been observed. 13% of total Zn in the topsoil can be regarded as mobile or easily mobilizable according to sequential chemical extractions (SCE). Zn concentrations of 10 mg/L were found in the soil water, where pH is acidic. Electron supply and the buffer capacity of the soil were identified as main factors controlling Zn mobility and release to the groundwater. Variable Pb concentrations up to 30 µg/L were observed in the soil water. In contrast to Zn, Pb is enriched in the mobile fraction of the oxidized topsoil by a factor of 2 compared to the subsoil with 2 g/kg Pb. 80% of the cation exchange capacity in the topsoil is occupied by Pb. Therefore, plant uptake and bioavailability are of major concern. If the site is not prevented from proceeding acidification in the future, a significant release of Zn, S, and Pb to the groundwater has to be expected. Results from this study show that the assessment of metal release especially from sulfide bearing anoxic material requires an extensive comprehension of leaching mechanisms on the one hand and on weathering processes, which influence the speciation and the mobility of metals, on the other hand. Processes, which may change redox and pH conditions in the future, have to be addressed to enable sound decisions for soil and groundwater protection and remediation.
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In this thesis I described the theory and application of several computational methods in solving medicinal chemistry and biophysical tasks. I pointed out to the valuable information which could be achieved by means of computer simulations and to the possibility to predict the outcome of traditional experiments. Nowadays, computer represents an invaluable tool for chemists. In particular, the main topics of my research consisted in the development of an automated docking protocol for the voltage-gated hERG potassium channel blockers, and the investigation of the catalytic mechanism of the human peptidyl-prolyl cis-trans isomerase Pin1.
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Krebs stellt eine der häufigsten Todesursachen in Europa dar. Grundlage für eine langfristige Verbesserung des Behandlungserfolgs ist ein molekulares Verständnis der Mechanismen, welche zur Krankheitsentstehung beitragen. In diesem Zusammenhang spielen Proteasen nicht nur eine wichtige Rolle, sondern stellen auch bei vielerlei Erkrankungen bereits anerkannte Zielstrukturen derzeitiger Behandlungsstrategien dar. Die Protease Threonin Aspartase 1 (Taspase1) spielt eine entscheidende Rolle bei der Aktivierung von Mixed Lineage Leukemia (MLL)-Fusionsproteinen und somit bei der Entstehung aggressiver Leukämien. Aktuelle Arbeiten unterstreichen zudem die onkologische Relevanz von Taspase1 auch für solide Tumore. Die Kenntnisse über die molekularen Mechanismen und Signalnetzwerke, welche für die (patho)biologischen Funktionen von Taspase1 verantwortlich sind, stellen sich allerdings noch immer als bruchstückhaft dar. Um diese bestehenden Wissenslücken zu schließen, sollten im Rahmen der Arbeit neue Strategien zur Inhibition von Taspase1 erarbeitet und bewertet werden. Zusätzlich sollten neue Einsichten in evolutionären Funktionsmechanismen sowie eine weitergehende Feinregulation von Taspase1 erlangt werden. Zum einen erlaubte die Etablierung und Anwendung eines zellbasierten Taspase1-Testsystem, chemische Verbindungen auf deren inhibitorische Aktivität zu testen. Überraschenderweise belegten solch zelluläre Analysen in Kombination mit in silico-Modellierungen eindeutig, dass ein in der Literatur postulierter Inhibitor in lebenden Tumorzellen keine spezifische Wirksamkeit gegenüber Taspase1 zeigte. Als mögliche Alternative wurden darüber hinaus Ansätze zur genetischen Inhibition evaluiert. Obwohl publizierte Studien Taspase1 als ααββ-Heterodimer beschreiben, konnte durch Überexpression katalytisch inaktiver Mutanten kein trans-dominant negativer Effekt und damit auch keine Inhibition des wildtypischen Enzyms beobachtet werden. Weiterführende zellbiologische und biochemische Analysen belegten erstmalig, dass Taspase1 in lebenden Zellen in der Tat hauptsächlich als Monomer und nicht als Dimer vorliegt. Die Identifizierung evolutionär konservierter bzw. divergenter Funktionsmechanismen lieferte bereits in der Vergangenheit wichtige Hinweise zur Inhibition verschiedenster krebsrelevanter Proteine. Da in Drosophila melanogaster die Existenz und funktionelle Konservierung eines Taspase1-Homologs postuliert wurde, wurde in einem weiteren Teil der vorliegenden Arbeit die evolutionäre Entwicklung der Drosophila Taspase1 (dTaspase1) untersucht. Obwohl Taspase1 als eine evolutionär stark konservierte Protease gilt, konnten wichtige Unterschiede zwischen beiden Orthologen festgestellt werden. Neben einem konservierten autokatalytischen Aktivierungsmechanismus besitzt dTaspase1 verglichen mit dem humanen Enzym eine flexiblere Substraterkennungs-sequenz, was zu einer Vergrößerung des Drosophila-spezifischen Degradoms führt. Diese Ergebnisse zeigen des Weiteren, dass zur Definition und Vorhersage des Degradoms nicht nur proteomische sondern auch zellbiologische und bioinformatische Untersuchungen geeignet und notwendig sind. Interessanterweise ist die differentielle Regulation der dTaspase1-Aktivität zudem auf eine veränderte intrazelluläre Lokalisation zurückzuführen. Das Fehlen von in Vertebraten hochkonservierten aktiven Kernimport- und nukleolären Lokalisationssignalen erklärt, weshalb dTaspase1 weniger effizient nukleäre Substrate prozessiert. Somit scheint die für die humane Taspase1 beschriebene Regulation von Lokalisation und Aktivität über eine Importin-α/NPM1-Achse erst im Laufe der Entwicklung der Vertebraten entstanden zu sein. Es konnte also ein bislang unbekanntes evolutionäres Prinzip identifiziert werden, über welches eine Protease einen Transport- bzw. Lokalisations-basierten Mechanismus zur Feinregulation ihrer Aktivität „von der Fliege zum Menschen“ nutzt. Eine weitere Möglichkeit zur dynamischen Funktionsmodulation bieten post-translationale Modifikationen (PTMs) der Proteinsequenz, zu welcher Phosphorylierung und Acetylierung zählen. Interessanterweise konnte für die humane Taspase1 über den Einsatz unabhängiger Methoden einschließlich massenspektrometrischer Analysen eine Acetylierung durch verschiedene Histon-Acetyltransferasen (HATs) nachgewiesen werden. Diese Modifikation erfolgt reversibel, wobei vor allem die Histon-Deacetylase HDAC1 durch Interaktion mit Taspase1 die Deacetylierung der Protease katalysiert. Während Taspase1 in ihrer aktiven Konformation acetyliert vorliegt, kommt es nach Deacetylierung zu einer Reduktion ihrer enzymatischen Aktivität. Somit scheint die Modulation der Taspase1-Aktivität nicht allein über intra-proteolytische Autoaktivierung, Transport- und Interaktionsmechanismen, sondern zudem durch post-translationale Modifikationen gesteuert zu werden. Zusammenfassend konnten im Rahmen dieser Arbeit entscheidende neue Einblicke in die (patho)biologische Funktion und Feinregulation der Taspase1 gewonnen werden. Diese Ergebnisse stellen nicht nur einen wichtigen Schritt in Richtung eines verbesserten Verständnis der „Taspase1-Biologie“, sondern auch zur erfolgreichen Inhibition und Bewertung der krebsrelevanten Funktion dieser Protease dar.