Development of a fluorescent-based single liposome assay for studying calcium transporter LMCA1

The morphological and functional unit of all the living organisms is the cell. The transmembrane proteins, localized in the plasma membrane of cells, play a key role in the survival of the cells themselves. These proteins perform a variety of different tasks, for example the control of the homeostasis. In order to control the homeostasis, these proteins have to regulate the concentration of chemical elements, like ions, inside and outside the cell. These regulations are fundamental for the survival of the cell and to understand them we need to understand how transmembrane proteins work. Two of the most important categories of transmembrane proteins are ion channels and transporter proteins. The ion channels have been depth studied at the single molecule level since late 1970s with the development of patch-clamp technique. It is not possible to apply this technique to study the transporter proteins so a new technique is under development in order to investigate the behavior of transporter proteins at the single molecule level. This thesis describes the development of a nanoscale single liposome assay for functional studies of transporter proteins based on quantitative fluorescence microscopy in a highly-parallel manner and in real time. The transporter of interest is the prokaryotic transporter Listeria Monocytogenes Ca2+-ATPase1 (LMCA1), a structural analogue of the eukaryotic calcium pumps SERCA and PMCA. This technique will allow the characterization of LMCA1 functionality at the single molecule level. Three systematically characterized fluorescent sensors were tested at the single liposome scale in order to investigate if their properties are suitable to study the function of the transporter of interest. Further studies will be needed in order to characterize the selected calcium sensor and pH sensor both implemented together in single liposomes and in presence of the reconstituted protein LMCA1.

Caratterizzazione di un setup miniaturizzato per studi di elettrofisiologia

La messa a punto di tecniche come il patch clamp e la creazione di doppi strati lipidici artificiali (artificial bilayers) ha permesso di effettuare studi su canali ionici per valutarne la permeabilità, la selettività ionica, la dipendenza dal voltaggio e la cinetica, sia in ambito di ricerca, per analizzarne il funzionamento specifico, sia in quello farmaceutico, per studiare la risposta cellulare a nuovi farmaci prodotti. Tali tecniche possono essere inoltre impiegate nella realizzazione di biosensori, combinando così i vantaggi di specificità e sensibilità dei sistemi biologici alla veloce risposta quantitativa degli strumenti elettrochimici. I segnali in corrente che vengono rilevati con questi metodi sono dell’ordine dei pA e richiedono perciò l’utilizzo di strumentazioni molto costose e ingombranti per amplificarli, analizzarli ed elaborarli correttamente. Il gruppo di ricerca afferente al professor Tartagni della facoltà di ingegneria di Cesena ha sviluppato un sistema miniaturizzato che possiede molte delle caratteristiche richieste per questi studi. L’obiettivo della tesi riguarda la caratterizzazione sperimentale di tale sistema con prove di laboratorio eseguite in uno spazio ridotto e senza l’impiego di ulteriori strumentazioni ad eccezione del PC. In particolare le prove effettuate prevedono la realizzazione di membrane lipidiche artificiali seguita dall’inserimento e dallo studio del comportamento di due particolari canali ionici comunemente utilizzati per questa tipologia di studi: la gramicidina A, per la facilità d’inserimento nella membrana e per la bassa conduttanza del singolo canale, e l’α-emolisina, per l’attuale impiego nella progettazione e realizzazione di biosensori. Il presente lavoro si sviluppa in quattro capitoli di seguito brevemente riassunti. Nel primo vengono illustrate la struttura e le funzioni svolte dalla membrana cellulare, rivolgendo particolare attenzione ai fosfolipidi e alle proteine di membrana; viene inoltre descritta la struttura dei canali ionici utilizzati per gli esperimenti. Il secondo capitolo comprende una descrizione del metodo utilizzato per realizzare i doppi strati lipidici artificiali, con riferimento all’analogo elettrico che ne risulta, ed una presentazione della strumentazione utilizzata per le prove di laboratorio. Il terzo e il quarto capitolo sono dedicati all’elaborazione dei dati raccolti sperimentalmente: in particolare vengono prima analizzati quelli specifici dell’amplificatore, quali quelli inerenti il rumore che si somma al segnale utile da analizzare e la variabilità inter-prototipo, successivamente si studiano le prestazioni dell’amplificatore miniaturizzato in reali condizioni sperimentali e dopo aver inserito i canali proteici all’interno dei bilayers lipidici.

Proprietà elettriche di cellule interagenti con matrici polimeriche biocompatibili

L'utilizzo di polimeri organici coniugati in dispositivi elettronici per applicazioni biologiche, grazie alle loro proprietà meccaniche ed elettriche, insieme alla loro biocompatibilità, è un campo di ricerca relativamente nuovo e in rapida espansione. In questo lavoro di tesi si utilizza la tecnica del Voltage Clamp in configurazione whole cell per caratterizzare le proprietà elettrofisiologiche della linea cellulare di glioblastoma multiforme (T98G) e per registrare le correnti ioniche di cellule adese su una matrice polimerica biocompatibile di poli(etilenediossitiofene)-poli(stirenesulfonato) (PEDOT:PSS). La tecnica consiste nel bloccare il potenziale di membrana al valore desiderato, secondo un preciso protocollo di stimolazione, misurando la corrente necessaria per mantenere costante il potenziale presente tra le due superfici della membrana cellulare. Nella prima parte del lavoro le cellule sono state perfuse con farmaci inibitori dei canali potassio, prima con il bloccante non specifico tetraetilammonio (TEA), e poi selettivamente tramite bloccanti specifici come iberiotossina e dendrotossina. Il 44% circa delle cellule ha evidenziato una significativa corrente residua riconducibile all'attività dei canali ionici voltaggio-dipendenti Kv1.2. Al contrario nelle cellule restanti questi canali non sono espressi. Successivamente, sempre utilizzando le T98G, si è analizzato come lo stato di ossido-riduzione del polimero coniugato PEDOT:PSS possa influenzare le correnti dei canali ionici di membrana; è emerso che il substrato di PEDOT:PSS ridotto provoca una diminuzione significativa della corrente registrata rispetto al substrato di controllo (petri in polistirene). Questi risultati sono stati confrontati con le curve di proliferazione delle cellule T98G coltivate per 24h, 48h e 72h sui diversi substrati considerati, evidenziando interessanti correlazioni nel caso del substrato PEDOT:PSS ridotto.

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.

Charge accumulation and transport in degenerately doped semiconducting polymers with mixed ionic and electronic conductivity

This thesis is part of the fields of Material Physics and Organic Electronics and aims to determine the charge carrier density and mobility in the hydrated conducting polymer–polyelectrolyte blend PEDOT:PSS. This kind of material combines electronic semiconductor functionality with selective ionic transport, biocompatibility and electrochemical stability in water. This advantageous material properties combination makes PEDOT:PSS a unique material to build organic electrochemical transistors (OECTs), which have relevant application as amplifying transducers for bioelectronic signals. In order to measure charge carrier density and mobility, an innovative 4-wire, contact independent characterization technique was introduced, the electrolyte-gated van der Pauw (EgVDP) method, which was combined with electrochemical impedance spectroscopy. The technique was applied to macroscopic thin film samples and micro-structured PEDOT:PSS thin film devices fabricated using photolithography. The EgVDP method revealed to be effective for the measurements of holes’ mobility in hydrated PEDOT:PSS thin films, which resulted to be <μ>=(0.67±0.02) cm^2/(V*s). By comparing this result with 2-point-probe measurements, we found that contact resistance effects led to a mobility overestimation in the latter. Ion accumulation at the drain contact creates a gate-dependent potential barrier and is discussed as a probable reason for the overestimation in 2-point-probe measurements. The measured charge transport properties of PEDOT:PSS were analyzed in the framework of an extended drift-diffusion model. The extended model fits well also to the non-linear response in the transport characterization and results suggest a Gaussian DOS for PEDOT:PSS. The PEDOT:PSS-electrolyte interface capacitance resulted to be voltage-independent, confirming the hypothesis of its morphological origin, related to the separation between the electronic (PEDOT) and ionic (PSS) phases in the blend.