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.

Aziridinazione stereoselettiva di chetoni α,β-insaturi α-sostituiti via organocatalisi

Il lavoro della presente Tesi è stato lo sviluppo della sintesi asimmetrica di aziridine chirali a partire da chetoni α,β-insaturi α-sostituiti, verificando la possibilità di applicare ammine primarie come organocatalizzatori attraverso un meccanismo tandem ione imminio-enammina. Nelle nostre prove le migliori ammine primarie si sono rivelate gli pseudoenantiomeri 9-ammino-9-deossi-epi-idrochinina e idrochinidina, e i migliori acidi per formare il sale catalitico sono stati acido trifluoroacetico (TFA) e acido salicilico. Il fattore chiave per le reazioni di aziridinazione è stata la scelta della molecola sorgente di azoto, che deve avere comportamento nucleofilico nel primo step di aza-Michael (via ione imminio), e comportamento elettrofilico nello step di chiusura del ciclo (via enammina). Le prove preliminari sono state condotte con il sale catalitico formato dalla 9-ammino-9-deossi-epi-idrochinina e TFA in toluene a 50 °C. Migliori risultati sono stati ottenuti sostituendo la sorgente di azoto utilizzata inizialmente e utilizzando il sale catalitico composto da 9-ammino-9-deossi-epi-idrochinidina e acido salicilico in toluene a 50 °C. In questo caso la resa è stata pari a 56% ed eccesso enantiomerico (ee) del 90%. Sfruttando quindi le condizioni ottimizzate inizialmente, abbiamo provato la reazione su altri due chetoni con maggiore ingombro sterico rispetto a quello utilizzato per l’ottimizzazione iniziale del processo. In entrambi i casi la reattività è stata sensibilmente inferiore a quanto atteso, con rese non superiori al 14%. Inoltre anche i valori di ee sono stati poco soddisfacenti. Ipotizziamo che questi risultati deludenti siano causati dall’ingombro sterico della catena in posizione β che impedisce l’avvicinamento del catalizzatore, il quale, non creando un intorno asimmetrico, non crea una distinzione tra le due possibili direzioni di attacco del nucleofilo. Da questi ultimi risultati sembra che la reazione di aziridinazione da noi ottimizzata sia per ora limitata al solo chetone utilizzato nella fase iniziale del lavoro. Al fine di estendere l’applicazione di queste condizioni, nel futuro saranno effettuate prove anche con altri chetoni α,β-insaturi α-sostituiti, ma che non presentino sostituzione in posizione β, dato che abbiamo osservato che essa rappresenta il maggiore limite per la reattività e selettività. Infine sarà importante determinare la configurazione assoluta del prodotto finora ottenuto, mediante spettroscopia ECD e VCD. E’ infatti importante conoscere tutte le caratteristiche chimiche e fisiche di prodotto ottenuto, in modo da avere maggiore conoscenza del processo da noi sviluppato, per poterlo migliorare ed estenderne l’applicabilità in futuro.

Applicazioni di 1-azadieni in cicloaddizioni di Diels-Alder enantioselettive organocatalizzate

Lo scopo di questo lavoro è stato quello di studiare dettagliatamente la reattività dell’N-benzilossicarbonil-1-aza-butadiene, utilizzando diversi dienofili in reazioni di Diels-Alder catalitiche enantioselettive promosse da organocatalizzatori bifunzionali in grado di dare interazioni deboli come legami a idrogeno. Questo 1-azadiene infatti può dare in linea di principio sia prodotti derivanti da reazioni di Diels-Alder a domanda elettronica diretta in cui funge da diene, sia reazioni a domanda elettronica inversa in cui il doppio legame terminale dell’1-azadiene, maggiormente reattivo in quanto meno ingombrato, funge da olefina elettronricca (reazione di Povarov). Per effettuare questo studio sono stati provati vari dienofili tra cui olefine elettron povere bi- e monosostituite che portavano alla degradazione del diene; derivati della malimmide e del pirazolo che davano cilcloaddotti derivanti dalla classica cicloaddizione [4+2] Diels-Alder con ottime conversioni in modo altamente diastereoselettivo, ma bassi eccessi enantiomerici ed infine si sono provate diverse immine che portavano al cicloaddotto della reazione di Povarov con ottimi risultati in termini di conversione e buoni eccessi enantiomerici. Quest’ultima applicazione che permette la sintesi di interessanti prodotti variamente funzionalizzabili, sarà oggetto di studio in futuro per ottimizzare le condizioni della reazione.

Idrossiamminazione asimmetrica di nitroolefine catalizzata da derivati degli alcaloidi della cinchona

Questo lavoro di tesi ha riguardato lo studio della reazione di addizione coniugata enantioselettiva di idrossilammine N-Cbz-protette a nitroolefine, attraverso l’utilizzo di una serie di catalizzatori organici bi-funzionali in grado di attivare contemporaneamente la nucleofilicità dell’idrossilammina, per mezzo di una reazione acido-base, e il trans-β-nitrostirene, attraverso interazione via legame a idrogeno.

Nuovi coniugati fra acido azelaico ed azaeterocicli: sintesi e valutazione dell'attività biologica

The well-known antiproliferative properties of the 9-hydroxystearic acid (9-HSA) on human colon cancer cells (HT-29 cell line) have inspired this thesis work in order to obtain new derivatives maintaining the C1-C8 chain of the HSA linked to an heterocyclic moiety at the C-9 carbon atom and to investigate their biological activity. First, thiazoles, thiadiazoles and benzothiazoles, that are compounds of interest in many fields for their biological activities, have been introduced through an amide bond starting from their 2-amino precursors. The products have been obtained by treatment with methyl 9-chloro-9-oxononanoate according to a Schotten-Baumann type reaction. The acylation reaction occurred at the endocyclic nitrogen atom of the heterocycle, as ascertained through NOESY-1D experiment. After, methyl 9-chloro-9-oxononanoate was reacted with indole, N-methylindole, and triptamine giving a serie of new indole derivatives. Finally, the biological activity of some compounds has been tested through assays on HT-29 cancer cells and bacterial and fungal microorganisms; docking calculations have also been performed to evaluate the possible interactions with the active site of histone deacetylase, which are molecular targets of the 9-HSA.

Direct C–H silylation and borylation of biomass derivatives by iridium heterogeneous catalysts

Furfural and its derivatives represent renewable and readily available platforms for a wide range of chemicals. Much attention has been devoted to their functionalization over the last years. TM-catalysed C–H activation has emerged as a powerful tool for synthesizing new C–C and C–X bonds. Moreover, it provides a sustainable way to obtain molecules by reducing waste and saving steps. At the same time, iridium catalysts have proven to be very active in some C–H functionalizations of several (hetero)arenes. Although very promising, this technique is still poorly applied on an industrial scale due to the severe conditions required. Continuous flow chemistry using heterogeneous catalysts appears to be a valuable way to overcome these problems. In this work, we present different solutions for the immobilization of homogeneous iridium complexes on silica gels, using bidentate amines and phosphines as anchoring ligands. We successfully employed the catalysts in C–H silylation and borylation of furfural, using C2 located directing group. In this way, we finally obtained a suitable catalyst that could be potentially applied in continuous-flow chemistry.