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.

Analisi comparativa di un circuito low pressure e high pressure EGR per un motore diesel sottostante a normativa americana US LEV III ULEV 125

Questa tesi di laurea nasce dall’esperienza maturata presso la VM Motori S.p.A., ufficio CRM (Centro Ricerca Motori) di ingegneria, divisione del reparto R&D (Research and Development) situato a Cento di Ferrara. Durante tale esperienza sono state affrontate le problematiche inerenti al settore automotive riguardo la ricerca e lo sviluppo dei motori endotermici diesel. Dopo un approccio introduttivo, che definisce l’ambito lavorativo in cui opera VM Motori S.p.A. e l’oggetto della tesi, si passa alla definizione ed alla calibrazione di un circuito low pressure EGR di un propulsore diesel da 200HP@3800rpm di potenza e 500Nm@1600rpm di coppia per uso automobilistico, mediante l’ausilio dei software AδαMO, INCA, Controldesk Next Generation, DoE, DIAdem ed INDICOM, software per lo studio della calibrazione al banco sviluppo. Si analizzano gli aspetti che contraddistinguono la VM Motori S.p.A. dalle altre aziende specializzate nel settore automotive, facendo riferimento ai campi produttivi in cui si applica l’ingegneria meccanica ed analizzandone gli aspetti tecnici, metodici e gestionali. Da notare il ruolo fondamentale delle automotive nell’economia mondiale in riferimento alla produzione dei principali propulsori diesel, primarie fonti produttive della VM.

Optimisation of chemical lysis protocol for point-of-care leukocyte differentiation

The full blood cell (FBC) count is the most common indicator of diseases. At present hematology analyzers are used for the blood cell characterization, but, recently, there has been interest in using techniques that take advantage of microscale devices and intrinsic properties of cells for increased automation and decreased cost. Microfluidic technologies offer solutions to handling and processing small volumes of blood (2-50 uL taken by finger prick) for point-of-care(PoC) applications. Several PoC blood analyzers are in use and may have applications in the fields of telemedicine, out patient monitoring and medical care in resource limited settings. They have the advantage to be easy to move and much cheaper than traditional analyzers, which require bulky instruments and consume large amount of reagents. The development of miniaturized point-of-care diagnostic tests may be enabled by chip-based technologies for cell separation and sorting. Many current diagnostic tests depend on fractionated blood components: plasma, red blood cells (RBCs), white blood cells (WBCs), and platelets. Specifically, white blood cell differentiation and counting provide valuable information for diagnostic purposes. For example, a low number of WBCs, called leukopenia, may be an indicator of bone marrow deficiency or failure, collagen- vascular diseases, disease of the liver or spleen. The leukocytosis, a high number of WBCs, may be due to anemia, infectious diseases, leukemia or tissue damage. In the laboratory of hybrid biodevices, at the University of Southampton,it was developed a functioning micro impedance cytometer technology for WBC differentiation and counting. It is capable to classify cells and particles on the base of their dielectric properties, in addition to their size, without the need of labeling, in a flow format similar to that of a traditional flow cytometer. It was demonstrated that the micro impedance cytometer system can detect and differentiate monocytes, neutrophils and lymphocytes, which are the three major human leukocyte populations. The simplicity and portability of the microfluidic impedance chip offer a range of potential applications in cell analysis including point-of-care diagnostic systems. The microfluidic device has been integrated into a sample preparation cartridge that semi-automatically performs erythrocyte lysis before leukocyte analysis. Generally erythrocytes are manually lysed according to a specific chemical lysis protocol, but this process has been automated in the cartridge. In this research work the chemical lysis protocol, defined in the patent US 5155044 A, was optimized in order to improve white blood cell differentiation and count performed by the integrated cartridge.

Clinical applicability of an US model to calculate the head blood outflow through collateral vessels.

Le vene giugulari interne sembrano essere la via principale attraverso cui il sangue defluisce dal cervello verso il cuore, quando siamo in posizione supina. Nel 2008 il professor Paolo Zamboni ha scoperto che una diminuzione dell'attività giugulare può portare allo sviluppo di una condizione emodinamica chiamata CCSVI. Questa può causare ipossia, ritardi nella perfusione cerebrale e riduzione del drenaggio dei cataboliti, oltre ad un'attivazione infiammatoria delle piccole vene e dei tessuti vicini. Questa condizione è stata da subito associata alla sclerosi multipla e su questo argomento si sono dibattuti molti gruppi di ricerca. Inoltre, altre patologie sembrano essere associate alla CCSVI, come il morbo di Parkinson, l'Alzheimer e la sindrome di Meniere. Proprio quest'ultima è uno degli argomenti che attualmente interessa di più il gruppo di lavoro in cui mi sono inserita. Questa patologia comporta problemi uditivi, come sordità e tinnito, vertigini e nausea. Il gruppo Vascolar Disease Center (VDC) dell'Università di Ferrara ha previsto per l'anno 2015 uno studio multicentrico, in cui si cercherà di verificare la correlazione tra CCSVI e sindrome di Meniere. La mia tesi fa parte di un studio preliminare a quello multicentrico. All'inizio del lavoro mi sono dedicata ad un'analisi critica di un modello emodinamico per la quantificazione dei flussi sanguigni: il modello BMC, pubblicato nel 2013 dal gruppo VDC, effettuando in parallelo una ricerca bibliografica sullo stato dell'arte in materia. In seguito ho cominciato a studiare off-line diversi studi patologici e fisiologici, in modo da prendere confidenza con gli strumenti e con le metodologie da utilizzare. Sono stata poi coinvolta dal gruppo VDC per partecipare attivamente al miglioramento del protocollo legato al modello BMC. Infine ho analizzato, con due metodologie differenti, 35 studi effettuati su pazienti otorinolaringoiatrici. Con i risultati ottenuti ho potuto effettuare diverse analisi statistiche al fine di verificare l'equivalenza delle due metodologie. L'obiettivo ultimo era quello di stabilire quale delle due fosse la tecnica migliore da utilizzare, successivamente, nello studio multicentrico.