Sviluppo e validazione sperimentale di strategie di previsione e controllo del fenomeno della preaccensione (Mega-Knock)

L’algoritmo per la previsione del Mega-Knock si inserisce all’interno di uno dei temi cardine dell’attuale ricerca nel campo motoristico: la minimizzazione del consumo di combustibile nei motori ad alto grado di sovralimentazione, sviluppati nell’ottica del downsizing. La possibilità di prevedere l’innescarsi del Mega-Knock consente di ottimizzare la definizione dell’obiettivo di titolo, evitando arricchimenti non necessari in un range di funzionamento del motore che frequentemente viene esplorato nella normale guida su strada. Si tratterà la possibilità di utilizzare una relazione empirica per cercare di arrivare alla previsione dell’insorgere della preaccensione, per poi ricorrere ad opportune strategie motore per evitare il verificarsi del fenomeno; il tutto tramite lo sviluppo di un algoritmo in ambiente MatLab-Simulink

Controlli non distruttivi su mega-coaster: risultati sperimentali e azioni correttive

Il lavoro di tesi è focalizzato sull'utilizzo dei controlli non distruttivi (NDT) nell'ambito della manutenzione industriale, in particolare al controllo di un mega-coaster. Dopo una breve panoramica sulle tecniche di indagine più utilizzate, si prosegue nell'ambito specifico dei controlli eseguiti all'interno del parco divertimenti di Mirabilandia, sull'attrazione di punta, ovvero l'inverted-coaster "KATUN". In particolare viene descritto il controllo del tracciato dell'attrazione, ovvero del binario, mediante tecnica ad ultrasuoni. L'elaborato si conclude con un riassunto dei risultati sperimentali ottenuti ed alcune azioni correttive intraprese per il miglioramento dell'efficacia dei controlli stessi.

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.

Un'applicazione mobile per controllo e monitoraggio della qualità dell'acqua di una piscina

Questo elaborato ha come argomento lo sviluppo di un progetto informatico creato per mettere in comunicazione tra di loro un sistema di gestione e controllo del ricambio di acqua in una piscina e un dispositivo mobile. Per la realizzazione del sistema di controllo è stata utilizzata una scheda Arduino Mega 2560 munita di modulo Ethernet, mentre, per quello che concerne il dispositivo mobile, la scelta è ricaduta su un device dotato di sistema operativo Android. La comunicazione tra questi due attori è mediata attraverso un server scritto in Java che gira nella stessa rete locale in cui è presente la scheda Arduino. Il progetto può essere inserito nell'ambito dell'Internet of Things, dove ogni oggetto è caratterizzato dalla possibilità di connettersi ad Internet e scambiare informazioni con ogni altro oggetto creando una rete. Questo progetto è suddiviso in tre parti: la prima si occupa della definizione di due protocolli di comunicazione tra le varie componenti, uno per lo scambio di messaggi tra client Android e Server Java e un secondo per quello tra scheda Arduino e Server; la seconda parte è incentrata sulla realizzazione del server Java che rende accessibile la scheda da qualsiasi luogo e permette la raccolta dei dati rilevanti provenienti dalla centralina. L’ultima parte infine è quella relativa allo sviluppo di una applicazione per Android che permette di monitorare il tutto e interagire con la centralina stessa.