Modelling, simulation and optimization of maintenance considerations on condition based maintenance

Globalization has increased the pressure on organizations and companies to operate in the most efficient and economic way. This tendency promotes that companies concentrate more and more on their core businesses, outsource less profitable departments and services to reduce costs. By contrast to earlier times, companies are highly specialized and have a low real net output ratio. For being able to provide the consumers with the right products, those companies have to collaborate with other suppliers and form large supply chains. An effect of large supply chains is the deficiency of high stocks and stockholding costs. This fact has lead to the rapid spread of Just-in-Time logistic concepts aimed minimizing stock by simultaneous high availability of products. Those concurring goals, minimizing stock by simultaneous high product availability, claim for high availability of the production systems in the way that an incoming order can immediately processed. Besides of design aspects and the quality of the production system, maintenance has a strong impact on production system availability. In the last decades, there has been many attempts to create maintenance models for availability optimization. Most of them concentrated on the availability aspect only without incorporating further aspects as logistics and profitability of the overall system. However, production system operator’s main intention is to optimize the profitability of the production system and not the availability of the production system. Thus, classic models, limited to represent and optimize maintenance strategies under the light of availability, fail. A novel approach, incorporating all financial impacting processes of and around a production system, is needed. The proposed model is subdivided into three parts, maintenance module, production module and connection module. This subdivision provides easy maintainability and simple extendability. Within those modules, all aspect of production process are modeled. Main part of the work lies in the extended maintenance and failure module that offers a representation of different maintenance strategies but also incorporates the effect of over-maintaining and failed maintenance (maintenance induced failures). Order release and seizing of the production system are modeled in the production part. Due to computational power limitation, it was not possible to run the simulation and the optimization with the fully developed production model. Thus, the production model was reduced to a black-box without higher degree of details.

La linea guida api - risk based inspection: Definizione delle frequenze di rilascio e ottimazione delle visite ispettive

La stima della frequenza di accadimento di eventi incidentali di tipo random da linee e apparecchiature è in generale effettuata sulla base delle informazioni presenti in banche dati specializzate. I dati presenti in tali banche contengono informazioni relative ad eventi incidentali avvenuti in varie tipologie di installazioni, che spaziano dagli impianti chimici a quelli petrolchimici. Alcune di queste banche dati risultano anche piuttosto datate, poiché fanno riferimento ad incidenti verificatisi ormai molto addietro negli anni. Ne segue che i valori relativi alle frequenze di perdita forniti dalle banche dati risultano molto conservativi. Per ovviare a tale limite e tenere in conto il progresso tecnico, la linea guida API Recommended Pratice 581, pubblicata nel 2000 e successivamente aggiornata nel 2008, ha introdotto un criterio per determinare frequenze di perdita specializzate alla realtà propria impiantistica, mediante l’ausilio di coefficienti correttivi che considerano il meccanismo di guasto del componente, il sistema di gestione della sicurezza e l’efficacia dell’attività ispettiva. Il presente lavoro di tesi ha lo scopo di mettere in evidenza l’evoluzione dell’approccio di valutazione delle frequenze di perdita da tubazione. Esso è articolato come descritto nel seguito. Il Capitolo 1 ha carattere introduttivo. Nel Capitolo 2 è affrontato lo studio delle frequenze di perdita reperibili nelle banche dati generaliste. Nel Capitolo 3 sono illustrati due approcci, uno qualitativo ed uno quantitativo, che permettono di determinare le linee che presentano priorità più alta per essere sottoposte all’attività ispettiva. Il Capitolo 4 è dedicato alla descrizione della guida API Recomended Practice 581. L’applicazione ad un caso di studio dei criteri di selezione delle linee illustrati nel Capitolo 3 e la definizione delle caratteristiche dell’attività ispettiva secondo la linea guida API Recomended Practice 581 sono illustrati nel Capitolo 5. Infine nel Capitolo 6 sono rese esplicite le considerazioni conclusive dello studio effettuato.

Analisi dei guasti di un termovalorizzatore

L’obiettivo del presente lavoro di tesi è stato quello di effettuare, tramite l’applicazione di una metodologia RBM – Risk Based Maintenance, l’analisi dei guasti avvenuti nel biennio 2012-2013 nel termovalorizzatore di rifiuti solidi urbani di Modena gestito dalla società Herambiente.

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.

World Class Manufacturing : approccio ad un sistema di manutenzione predittiva (CBM)

L’oggetto di analisi del presente lavoro di tesi è il modello di Operational Excellence noto come World Class Manufacturing in particolare l’approccio allo step 6 del pilastro Professional Maintenance, dove si richiede l’implementazione di un sistema di manutenzione PREDITTIVA, la cosiddetta CBM (Conditional Based Maintenance) . Il modello a cui si fa riferimento fu teorizzato dal professore giapponese H. Yamashina verso la metà degli anni 2000 e giunse in Italia attorno al 2005, quando Fiat Group (oggi FCA) lo adottò come approccio standard alla gestione della produzione. Questo tipo di analisi, orientata verso una prospettiva pratica più che teorica, deriva direttamente da un’esperienza sul campo che ho svolto all’interno di un’azienda che ha aderito al World Class Manufacturing (WCM). Nel capitolo 1 verrà proposto un excursus delle metodologie alla base del WCM e del percorso storico che ha portato alla formulazione del modello. Nel secondo capitolo verrà proposto un caso di applicazione del WCM all'interno di un Gruppo, nella fattispecie Ariston Thermo Group (ATG). Dopo un’overview sul Gruppo e sulla storia della sua adesione al programma di miglioramento, la trattazione si focalizza sull'approccio di ATG al WCM. Nel terzo capitolo verrà introdotta la Manutenzione Professionale secondo le principali politiche manutentive schematizzate dal WCM. Verranno presentate singolarmente per sottolineare i loro obiettivi seguiti dai vantaggi e svantaggi che si possono ottenere nell’implementare ogni singola politica. Nel quarto capitolo verranno specificate sotto un aspetto prettamente pratico le varie attività svolte dalla PM così da evidenziare lo sviluppo e il miglioramento continuo che essa sta ottenendo dall’introduzione del WCM; principalmente la presentazione delle varie attività si riferiscono al passaggio allo step 6 della PM, dove verrà presentata approfonditamente elencando e analizzando tutte le attività svolte per approcciarsi alla CBM.