18 resultados para Multiple view integration
em AMS Tesi di Laurea - Alm@DL - Università di Bologna
Resumo:
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.
Resumo:
La gestione di sorgenti multiple di disturbo in AMP: il caso delle Isole Tremiti Il seguente lavoro di tesi valuta l’efficacia di protezione di un’area marina protetta (AMP) sui popolamenti di differenti habitat compresi in zone a diverso regime di tutela. Questo tema è molto sentito sia dal punto di vista scientifico, poiché le AMP rappresentano uno esperimento di esclusione delle attività antropiche ad ampia scala, sia dal punto di vista socio-economico per l’interesse che sono in grado di generare nelle comunità locali. Tuttavia, ad oggi, gli studi che abbiano dimostrato l’efficacia di protezione delle AMP sono pochi e sono per lo più diretti sulle specie di maggior interesse commerciale. In generale, c’è un’evidente mancanza di protezione in molte AMP del Mediterraneo e di aree extra-mediterranee che può essere attribuita a diversi fattori, tra cui le caratteristiche fisiche dei siti dove sono state istituite, le modalità di gestione e le numerose attività illegali che vengono svolte all’interno dei loro confini. Inoltre, nelle aree protette, spesso, anche le attività lecite non sono adeguatamente regolamentate, limitando ulteriormente il perseguimento degli obiettivi istitutivi e la tutela della biodiversità marina. Testare le ipotesi sull’efficacia di protezione delle AMP è, quindi, di fondamentale importanza per capire quali tipi di impatti sono maggiormente presenti e per poter fornire agli Enti gestori informazioni utili per migliorare l’amministrazione delle AMP. In particolare, l’AMP dell’arcipelago delle Isole Tremiti, istituita da oltre venti anni, è un’area protetta che presenta molte criticità, come dimostrato in precedenti campagne di monitoraggio condotte dal Consorzio Nazionale Interuniversitario per le Scienze del Mare (CoNISMa). In questo contesto, la presente tesi è stata sviluppata con lo scopo di quantificare l’effetto della regolamentazione di diverse attività umane sui popolamenti del subtidale, della frangia e delle praterie di Posidonia oceanica nell’AMP delle Isole Tremiti a diverse scale spaziali per un periodo di circa dieci anni. Questo lavoro, inoltre, rientra in un progetto finanziato dal Ministero dell’Ambiente e della Tutela del Territorio e del Mare al CoNISMa volto ad impostare un’attività di monitoraggio sperimentale e di mitigazione in questa AMP. I campionamenti sono stati condotti tra Giugno e Settembre 2010 e i dati raccolti sono stati integrati a quelli ottenuti nei precedenti monitoraggi svolti nelle Isole Tremiti. I risultati hanno mostrato che: 1) ci sono differenze significative consistenti nel tempo tra il subtidale dell’isola di Pianosa e quello delle altre isole dell’arcipelago; 2) i popolamenti nella frangia di Pianosa, di San Domino e di Caprara non presentano differenze significative; 3) c’è un’elevata variabilità a scala di sito nelle praterie di Posidonia oceanica, ma non si osserva una differenza tra località protette ed impattate. La differenza riscontrata nel subtidale tra zona a protezione integrale (Pianosa) e le altre isole dell’arcipelago (controlli) non è però attribuibile ad un effetto della protezione. Infatti, il subtidale di Pianosa è caratterizzato da un barren molto esteso con elevate percentuali di spugne rosse incrostanti, di alghe rodoficee incrostanti e di ricci di mare, mentre nelle isole di San Domino e di Caprara c’è una maggiore diversità data da alghe corallinacee articolate, alghe erette, idrozoi, ascidiacei e numerose spugne. Diversi fattori possono aver agito nel determinare questo risultato, ma molto probabilmente la cospicua attività di pesca illegale che viene praticata a Pianosa combinata all’attività di grazing degli erbivori, non controllati dai predatori, limita il recupero dei popolamenti. Al contrario, l’assenza di differenze nei popolamenti della frangia delle tre isole campionate fa ipotizzare la mancanza di impatti diretti (principalmente il calpestio) su questo habitat. Per quanto riguarda la Posidonia oceanica i risultati suggeriscono che si stia verificando un ancoraggio indiscriminato su tutte le praterie delle Isole Tremiti e che molto probabilmente si tratta di praterie in forte regressione, come indicano anche le ricerche condotte dall’Università di Bari. C’è bisogno, tuttavia, di ulteriori studi che aiutino a comprendere meglio la variabilità nella riposta dei popolamenti in relazione alle diverse condizioni ambientali e al diverso sforzo di gestione. In conclusione, dai risultati ottenuti, emerge chiaramente come anche nell’AMP delle Isole Tremiti, ci sia una scarsa efficacia di protezione, così come è stato rilevato per la maggior parte delle AMP italiane. Per risolvere le costanti conflittualità che perdurano nelle Isole Tremiti e che non permettono il raggiungimento degli obiettivi istitutivi dell’AMP, è assolutamente necessario, oltre che far rispettare la regolamentazione vigente incrementando il numero di guardacoste sull’isola durante tutto l’anno, procedere, eventualmente, ad una rizonizzazione dell’AMP e sviluppare un piano di gestione in accordo con la popolazione locale adeguatamente sensibilizzata. Solo in questo modo sarà possibile ridurre le numerose attività illegali all’interno dell’AMP, e, allo stesso tempo, rendere gli stessi cittadini una componente imprescindibile della conservazione di questo arcipelago.
Resumo:
The first part of my work consisted in samplings conduced in nine different localities of the salento peninsula and Apulia (Italy): Costa Merlata (BR), Punta Penne (BR), Santa Cesarea terme (LE), Santa Caterina (LE), Torre Inserraglio (LE), Torre Guaceto (BR), Porto Cesareo (LE), Otranto (LE), Isole Tremiti (FG). I collected data of species percentage covering from the infralittoral rocky zone, using squares of 50x50 cm. We considered 3 sites for location and 10 replicates for each site, which has been taken randomly. Then I took other data about the same places, collected in some years, and I combined them together, to do a spatial analysis. So I started from a data set of 1896 samples but I decided not to consider time as a factor because I have reason to think that in this period of time anthropogenic stressors and their effects (if present), didn’t change considerably. The response variable I’ve analysed is the covering percentage of an amount of 243 species (subsequently merged into 32 functional groups), including seaweeds, invertebrates, sediment and rock. 2 After the sampling, I have been spent a period of two months at the Hopkins Marine Station of Stanford University, in Monterey (California,USA), at Fiorenza Micheli's laboratory. I've been carried out statistical analysis on my data set, using the software PRIMER 6. My explorative analysis starts with a nMDS in PRIMER 6, considering the original data matrix without, for the moment, the effect of stressors. What comes out is a good separation between localities and it confirms the result of ANOSIM analysis conduced on the original data matrix. What is possible to ensure is that there is not a separation led by a geographic pattern, but there should be something else that leads the differences. Is clear the presence of at least three groups: one composed by Porto cesareo, Torre Guaceto and Isole tremiti (the only marine protected areas considered in this work); another one by Otranto, and the last one by the rest of little, impacted localities. Inside the localities that include MPA(Marine Protected Areas), is also possible to observe a sort of grouping between protected and controlled areas. What comes out from SIMPER analysis is that the most of the species involved in leading differences between populations are not rare species, like: Cystoseira spp., Mytilus sp. and ECR. Moreover I assigned discrete values (0,1,2) of each stressor to all the sites I considered, in relation to the intensity with which the anthropogenic factor affect the localities. 3 Then I tried to estabilish if there were some significant interactions between stressors: by using Spearman rank correlation and Spearman tables of significance, and taking into account 17 grades of freedom, the outcome shows some significant stressors interactions. Then I built a nMDS considering the stressors as response variable. The result was positive: localities are well separeted by stressors. Consequently I related the matrix with 'localities and species' with the 'localities and stressors' one. Stressors combination explains with a good significance level the variability inside my populations. I tried with all the possible data transformations (none, square root, fourth root, log (X+1), P/A), but the fourth root seemed to be the best one, with the highest level of significativity, meaning that also rare species can influence the result. The challenge will be to characterize better which kind of stressors (including also natural ones), act on the ecosystem; and give them a quantitative and more accurate values, trying to understand how they interact (in an additive or non-additive way).
Resumo:
The ability to represent the transport and fate of an oil slick at the sea surface is a formidable task. By using an accurate numerical representation of oil evolution and movement in seawater, the possibility to asses and reduce the oil-spill pollution risk can be greatly improved. The blowing of the wind on the sea surface generates ocean waves, which give rise to transport of pollutants by wave-induced velocities that are known as Stokes’ Drift velocities. The Stokes’ Drift transport associated to a random gravity wave field is a function of the wave Energy Spectra that statistically fully describe it and that can be provided by a wave numerical model. Therefore, in order to perform an accurate numerical simulation of the oil motion in seawater, a coupling of the oil-spill model with a wave forecasting model is needed. In this Thesis work, the coupling of the MEDSLIK-II oil-spill numerical model with the SWAN wind-wave numerical model has been performed and tested. In order to improve the knowledge of the wind-wave model and its numerical performances, a preliminary sensitivity study to different SWAN model configuration has been carried out. The SWAN model results have been compared with the ISPRA directional buoys located at Venezia, Ancona and Monopoli and the best model settings have been detected. Then, high resolution currents provided by a relocatable model (SURF) have been used to force both the wave and the oil-spill models and its coupling with the SWAN model has been tested. The trajectories of four drifters have been simulated by using JONSWAP parametric spectra or SWAN directional-frequency energy output spectra and results have been compared with the real paths traveled by the drifters.
Resumo:
Opportunistic diseases caused by Human Immunodeficiency Virus (HIV) and Hepatitis B Virus (HBV) is an omnipresent global challenge. In order to manage these epidemics, we need to have low cost and easily deployable platforms at the point-of-care in high congestions regions like airports and public transit systems. In this dissertation we present our findings in using Localized Surface Plasmon Resonance (LSPR)-based detection of pathogens and other clinically relevant applications using microfluidic platforms at the point-of-care setting in resource constrained environment. The work presented here adopts the novel technique of LSPR to multiplex a lab-on-a-chip device capable of quantitatively detecting various types of intact viruses and its various subtypes, based on the principle of a change in wavelength occurring when metal nano-particle surface is modified with a specific surface chemistry allowing the binding of a desired pathogen to a specific antibody. We demonstrate the ability to detect and quantify subtype A, B, C, D, E, G and panel HIV with a specificity of down to 100 copies/mL using both whole blood sample and HIV-patient blood sample discarded from clinics. These results were compared against the gold standard Reverse Transcriptase Polymerase Chain Reaction (RT-qPCR). This microfluidic device has a total evaluation time for the assays of about 70 minutes, where 60 minutes is needed for the capture and 10 minutes for data acquisition and processing. This LOC platform eliminates the need for any sample preparation before processing. This platform is highly multiplexable as the same surface chemistry can be adapted to capture and detect several other pathogens like dengue virus, E. coli, M. Tuberculosis, etc.
Resumo:
Analisi e sviluppo di procedure di importazione dati per un integratore di annunci immobiliari dedicato alla vendita di soggiorni turistici in case vacanza. Il documento tratta inoltre l'implementazione di un Web Service conforme all'architettura RESTful per l'accesso e l'esportazione dei dati a soggetti terzi autorizzati tramite Digest Authentication.
Resumo:
This dissertation document deals with the development of a project, over a span of more than two years, carried out within the scope of the Arrowhead Framework and which bears my personal contribution in several sections. The final part of the project took place during a visiting period at the university of Luleå. The Arrowhead Project is an European project, belonging to the ARTEMIS association, which aims to foster new technologies and unify the access to them into an unique framework. Such technologies include the Internet of Things phe- nomenon, Smart Houses, Electrical Mobility and renewable energy production. An application is considered compliant with such framework when it respects the Service Oriented Architecture paradigm and it is able to interact with a set of defined components called Arrowhead Core Services. My personal contribution to this project is given by the development of several user-friendly API, published in the project's main repository, and the integration of a legacy system within the Arrowhead Framework. The implementation of this legacy system was initiated by me in 2012 and, after many improvements carried out by several developers in UniBO, it has been again significantly modified this year in order to achieve compatibility. The system consists of a simulation of an urban scenario where a certain amount of electrical vehicles are traveling along their specified routes. The vehicles are con-suming their battery and, thus, need to recharge at the charging stations. The electrical vehicles need to use a reservation mechanism to be able to recharge and avoid waiting lines, due to the long recharge process. The integration with the above mentioned framework consists in the publication of the services that the system provides to the end users through the instantiation of several Arrowhead Service Producers, together with a demo Arrowhead- compliant client application able to consume such services.
Resumo:
L’aumento dei consumi energetici e la sempre maggiore attenzione posta al tema ambientale fanno delle energie alternative una valida alternativa alle fonti , quali carbone e petrolio,che presentano una elevata generazione di gas serra . Tra le varie fonti alternative di energia un ruolo preponderante è stato assunto dal solare fotovoltaico, che dagli anni ’80 ad oggi ha conosciuto un rapido sviluppo sia in termini di ricerca che di utilizzo su larga scala. Negli ultimi anni tutti gli studi si stanno concentrando su un nuovo tipo di fotovoltaico, quello di terza generazione , il cui scopo è quello di ottenere dispositivi che possano garantire elevate efficienze in modo tale che la tecnologia fotovoltaica sia in grado di affermarsi definitivamente nel settore dell’energia. Il presente lavoro di tesi analizza il processo di conversione fotovoltaica ed il principio di funzionamento delle celle solari . I limiti termodinamici per l'efficienza di conversione di celle solari a singola giunzione sono stati discussi nella tesi. E' presentata nella tesi una rassegna delle principali strategie per il superamento dei limiti termodinamici per l'efficienza di una cella solare a singola giunzione . Sono stati analizzati : •il processo di rilassamento intrabanda dei nanocristalli ; •la generazione multipla di eccitoni (MEG) •il processo di Generazione di eccitoni multipli in nanocristalli di silicio colloidali (MEG in Si NCs). Tali risultati rivestono un particolare interesse per lo sviluppo di celle solari innovative , ad alta efficienza di conversione , utilizzando un materiale facilmente reperibile ed economico come appunto è il Silicio.
Resumo:
The present thesis work proposes a new physical equivalent circuit model for a recently proposed semiconductor transistor, a 2-drain MSET (Multiple State Electrostatically Formed Nanowire Transistor). It presents a new software-based experimental setup that has been developed for carrying out numerical simulations on the device and on equivalent circuits. As of 2015, we have already approached the scaling limits of the ubiquitous CMOS technology that has been in the forefront of mainstream technological advancement, so many researchers are exploring different ideas in the realm of electrical devices for logical applications, among them MSET transistors. The idea that underlies MSETs is that a single multiple-terminal device could replace many traditional transistors. In particular a 2-drain MSET is akin to a silicon multiplexer, consisting in a Junction FET with independent gates, but with a split drain, so that a voltage-controlled conductive path can connect either of the drains to the source. The first chapter of this work presents the theory of classical JFETs and its common equivalent circuit models. The physical model and its derivation are presented, the current state of equivalent circuits for the JFET is discussed. A physical model of a JFET with two independent gates has been developed, deriving it from previous results, and is presented at the end of the chapter. A review of the characteristics of MSET device is shown in chapter 2. In this chapter, the proposed physical model and its formulation are presented. A listing for the SPICE model was attached as an appendix at the end of this document. Chapter 3 concerns the results of the numerical simulations on the device. At first the research for a suitable geometry is discussed and then comparisons between results from finite-elements simulations and equivalent circuit runs are made. Where points of challenging divergence were found between the two numerical results, the relevant physical processes are discussed. In the fourth chapter the experimental setup is discussed. The GUI-based environments that allow to explore the four-dimensional solution space and to analyze the physical variables inside the device are described. It is shown how this software project has been structured to overcome technical challenges in structuring multiple simulations in sequence, and to provide for a flexible platform for future research in the field.
Resumo:
Nell'era genomica moderna, la mole di dati generata dal sequenziamento genetico è diventata estremamente elevata. L’analisi di dati genomici richiede l’utilizzo di metodi di significatività statistica per quantificare la robustezza delle correlazioni individuate nei dati. La significatività statistica ci permette di capire se le relazioni nei dati che stiamo analizzando abbiano effettivamente un peso statistico, cioè se l’evento che stiamo analizzando è successo “per caso” o è effettivamente corretto pensare che avvenga con una probabilità utile. Indipendentemente dal test statistico utilizzato, in presenza di test multipli di verifica (“Multiple Testing Hypothesis”) è necessario utilizzare metodi per la correzione della significatività statistica (“Multiple Testing Correction”). Lo scopo di questa tesi è quello di rendere disponibili le implementazioni dei più noti metodi di correzione della significatività statistica. È stata creata una raccolta di questi metodi, sottoforma di libreria, proprio perché nel panorama bioinformatico moderno non è stato trovato nulla del genere.