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.

Mitigazione sequestro e stoccaggio di diossido di carbonio

The main objective of my thesis was the technical-economic feasibility of a system of electricity generation integrated with CCS. The policy framework for development processing is part of the recent attention that at the political level has been directed towards the use of CCS technologies with the aim of addressing the problems of actual climate change. Several technological options have been proposed to stabilize and reduce the atmospheric concentrations of carbon dioxide (CO2) among which, the most promising for IPPC (Intergovernmental Panel on Climate Change)are the CCS technologies (Carbon Capture and Storage & Carbon Capture and Sequestration). The remedy proposed for large stationary CO2 sources as thermoelectric power plants is to separate the flue gas capturing CO2 and to store it into deep subsurface geological formations (more than 800 meters of depth). In order to support the identification of potential CO2 storage reservoirs in Italy and in Europe by Geo Capacity(an European database) new studies are developing. From the various literature data analyzed shows that most of the CO2 emitted from large stationary sources comes from the processes of electricity generation (78% of total emissions) and from (about 60%) those using coal especially. The CCS have the objective of return "to the sender" , the ground, the carbon in oxidized form (CO2) after it has been burned by man starting from its reduced form (CH4, oil and coal), then the carbon dioxide is not a "pollutant" if injected into the subsurface, CO2 is an acid reagent that interacts with the rock, with underground fluid and the characteristics of the host rock. The results showed that the CCS technology are very urgent, because unfortunately there are too many industrial sources of CO2 in assets (power plants, refineries, cement plants, steel mills) in the world who are carrying too quickly the CO2 atmospheric concentration levels to values that aren't acceptable for our dear planet.

Reazioni di vari reagenti elettrofili con derivati amminotiazolici ad elevato potere nucleofilo

The nucleophile/electrophile combination in the aromatic substitution reaction using aminothiazole derivatives as nucleophiles has been the subject of this study. The reaction between 2,4-dipyrrolidinylthiazole and the neutral carbon electrophile 1,3,5-trinitrobenzene gave a stable Wheland-Meisenheimer (WM) complex. This represents another example, among those already found by the research group in which this work has been carried out, of stable zwitterionic σ-intermediates. When the reaction was carried out with halonitrobenzene derivatives, it produced the substitution product in position 5 of the thiazole ring. 2,4-dipyrrolidinylthiazole and arenediazonium salts gave the coupling product at the C5 of the thiazole ring together with many byproducts and the stable Wheland intermediate formed by attack of the proton on the C5 of the starting thiazole reagent. Arenediazonium salts were coupled also with 2-pyrrolidinylthiazole. In this case quantitative formation of the substitution product deriving from the attack of the electrophile on the carbon nucleophilic position of the thiazole ring was obtained. In conclusion, the results had allowed to expand the knowledge on electrophilic/nucleophilic interactions in the aromatic substitution involving thiazole heteroaromatics and provided a further example of stable Wheland-Meisenheimer intermediates.

Sintesi e caratterizzazione di prepolimeri per resine epossidiche derivanti da fonti rinnovabili e naturali attraverso un processo a basso impatto ambientale

La sostituzione di materie prime provenienti da risorse fossili con biomasse rinnovabili, utilizzando un processo a basso impatto ambientale, è una delle più importanti sfide della "Green Chemistry". Allo stesso tempo, la sintesi di resine epossidiche fornisce la chiave per la realizzazione di materiali ad alto valore aggiunto. Tuttavia, ad oggi, il 90% della produzione di resine epossidiche è basato sull'uso di bisfenolo A, che ha effetti di xenoestrogeno, ed epicloridrina, tossica e cancerogena. Su queste basi, è stata individuata una strategia sintetica per la sintesi di prepolimeri innovativi per resine epossidiche, che utilizza come substrato di reazione diidrossibenzeni di origine naturale ed evita l'uso di epicloridrina e altri reagenti tossici o pericolosi. La suddetta strategia sintetica è basata sulla sequenza: allilazione dei diidrossibenzeni - epossidazione dei doppi legami ottenuti. In questa procedura non vengono utilizzati drastiche condizioni di reazione e il solvente è acqua, con una catalisi di trasferimento di fase o, in aggiunte di acetonitrile, in un sistema bifasico. La resa complessiva dei due “step” dipende dalla posizione dei due ossidrili nei diidrossibenzeni. Il reagente che porta la resa massima è l’idrochinone (1,4 diidrossibenzene), che, come riportato in letteratura, permette la formazione di resine epossidiche con proprietà simili alle resine di epicloridrina e bisfenolo A. The substitution of raw materials from fossil fuels with renewable biomass using a low environmental impact process is one of the greatest challenges of the "Green Chemistry". At the same time, the synthesis of epoxy resins provides the key to the realization of high added value materials. However, 90% of the production of epoxy resins is based on the use of bisphenol A, a xenoestrogen, and epichlorohydrin, that is toxic and carcinogenic. On these bases, a synthetic strategy for the synthesis of innovative prepolymers of epoxy resins, that uses dihydroxybenzenes of natural origin as reaction substrates and avoids the use of epichlorohydrin and other toxic or dangerous reagents has been identified. The above synthetic strategy is based on the sequence: allylation of dihydroxybenzenes - epoxidation of the double bonds obtained. In this procedure, drastic reaction conditions are dismissed and the solvent used is water with a phase transfer catalysis or, in addition, acetonitrile in a biphasic system. The overall yield of the two steps depends on the position of the two hydroxyls of the dihydroxybenzenes. The reagent that leads to the highest yield is hydroquinone (1,4 dihydroxybenzene), which, as reported in literature, allows the formation of epoxy resins with similar properties to the resins from bisphenol A and epichlorohydrin.

Sintesi di PNA a libertà conformazionale ridotta

The present work started a research project aimed at the synthesis of conformationally “locked” PNA (Peptide Nucleic Acids) monomers. Compared to classic aeg-PNA, this structural modification would result in an improvement in the pairing properties with natural nucleic acids, due to entropic variations in the process. Specifically, an attempt was made to build a PNA monomer around a β-lactam ring. That ring could be imagined as obtained by linking the methylene groups in α position of both the nucleobase and the carboxyl function. These structural properties would imply pre-organization of the final oligomer, improving the pairing process in biological systems. The first step of this work was the investigation of the Staudinger reaction for the ciclization of the lactam ring, and in particular the activation method of the carboxylic group of the nucleobase derivatives. Use of triazine chloride led to the synthesis of the adenine-based β-lactam-PNA. Attempts to synthesize the same monomer based on cytosine, guanine and thymine were unsuccessful, so alternative methods for carboxylic group activation were investigated. Conversion of carboxylic acids to acyl chlorides led to a partial result: despite the method worked well with analogues of the final reactants, it didn’t worked with substrates needed for lactam based PNAs. Search for a valid activation process continued involving carbonyl diimidazole, Mukayama reagent, and LDA (with methylester derivative of nucelobase) without good results. Last, it was investigated a different synthetic approach by first synthesizing a proper backbone with a chlorine in the β- lactam ring. This chlorine ring should undergo substitution by a nucleobase anion to give the desired PNA monomer. Unluckily also this synthetic route didn’t lead to the desired monomers.

Studio dell'interazione di etanolo con catalizzatori TiO2-CeOx.

Due to the limited availability of natural oil and the harmful effects of its usage, the industry has focused in searching for sustainable types of raw materials for the production of chemicals. The bioethanol, obtained by fermentation of biomass, has gained particular importance in recent years both as a biofuel, and as a “building block” molecule because it can be considered as a starting reagent to obtain other added value chemical compounds, such as ethylene, acetaldehyde, butadiene and ethyl acetate. The goal of this research was the study of the interaction of ethanol with catalysts based on TiO2-CeOX. Since the electronic properties have implications on the catalytic activity, the idea was to understand if the TiO2-CeOX systems have different reactivity from that of ceria and rutile alone, or an intermediate between them. The study was focused on the characterization of the adsorbed species on the catalysts surface after ethanol adsorption through an in-situ spectroscopic technique (DRIFTS) that allowed us to extract information that could be helpful for the understanding of the processes at the molecular level. The mass spectrometry was used to monitor on-line the desorbed products. Furthermore, reactivity tests in a flow reactor were performed, in order to verify the catalytic behavior of the samples in conditions which are more similar to those applied at an industrial scale. The samples showed to behave in different way depending on the conditions used and the thermal treatment. The particular behavior of the mixed samples with respect to the single oxides is interpreted for each case according to the spectroscopic information collected.

Catalytic decomposition of formic acid using supported metal nanoparticles

Upgrade of hydrogen to valuable fuel is a central topic in modern research due to its high availability and low price. For the difficulties in hydrogen storage, different pathways are still under investigation. A promising way is in the liquid-phase chemical hydrogen storage materials, because they can lead to greener transformation processes with the on line development of hydrogen for fuel cells. The aim of my work was the optimization of catalysts for the decomposition of formic acid made by sol immobilisation method (a typical colloidal method). Formic acid was selected because of the following features: it is a versatile renewable reagent for green synthesis studies. The first aim of my research was the synthesis and optimisation of Pd nanoparticles by sol-immobilisation to achieve better catalytic performances and investigate the effect of particle size, oxidation state, role of stabiliser and nature of the support. Palladium was chosen because it is a well-known active metal for the catalytic decomposition of formic acid. Noble metal nanoparticles of palladium were immobilized on carbon charcoal and on titania. In the second part the catalytic performance of the “homemade” catalyst Pd/C to a commercial Pd/C and the effect of different monometallic and bimetallic systems (AuxPdy) in the catalytic formic acid decomposition was investigated. The training period for the production of this work was carried out at the University of Cardiff (Group of Dr. N. Dimitratos).