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.

An experimental and modelling study of the capture of CO2 from gas mixtures with different techniques, with focus on multicomponent effects.

In the present work, the deviations in the solubility of CO2, CH4, and N2 at 30 °c in the mixed gases (CO2/CH4) and (CO2/N2) from the pure gas behavior were studied using the dual-mode model over a wide range of equilibrium composition and pressure values in two glassy polymers. The first of which was PI-DAR which is the polyimide formed by the reaction between 4, 6-diaminoresorcinol dihydrochloride (DAR-Cl) and 2, 2’-bis-(3, 4-dicarboxyphenyl) hexafluoropropane dianhydride (6FDA). The other glassy polymer was TR-DAR which is the corresponding thermally rearranged polymer of PI-DAR. Also, mixed gas sorption experiments for the gas mixture (CO2/CH4) in TR-DAR at 30°c took place in order to assess the degree of accuracy of the dual-mode model in predicting the true mixed gas behavior. The experiments were conducted on a pressure decay apparatus coupled with a gas chromatography column. On the other hand, the solubility of CO2 and CH4 in two rubbery polymers at 30⁰c in the mixed gas (CO2/CH4) was modelled using the Lacombe and Sanchez equation of state at various values of equilibrium composition and pressure. These two rubbery polymers were cross-linked poly (ethylene oxide) (XLPEO) and poly (dimethylsiloxane) (PDMS). Moreover, data about the sorption of CO2 and CH4 in liquid methyl dietahnolamine MDEA that was collected from literature65-67 was used to determine the deviations in the sorption behavior in the mixed gas from that in the pure gases. It was observed that the competition effects between the penetrants were prevailing in the glassy polymers while swelling effects were predominant in the rubbery polymers above a certain value of the fugacity of CO2. Also, it was found that the dual-mode model showed a good prediction of the sorption of CH4 in the mixed gas for small pressure values but in general, it failed to predict the actual sorption of the penetrants in the mixed gas.

Confezionamento di uova con guscio in atmosfera protettiva: Studio degli indici di freschezza e delle proprieta tecnologiche dei suoi costituenti

L’uovo è considerato l’alimento più completo dal punto di vista nutrizionale e allo stesso tempo è altamente deperibile con perdita rapida delle caratteristiche qualitative. Esso infatti interagisce con l’atmosfera circostante determinando perdita di vapore d’acqua e CO2 dal guscio. La diffusione di CO2 comincia immediatamente dopo la deposizione con un conseguente rapido aumento di pH, soprattutto nell’albume che determina maggiori rischi di contaminazione microbica. La regolamentazione dell’Unione Europea non permette l’utilizzo di interventi stabilizzanti tradizionali (lavaggio o conservazione refrigerata) sulle uova fresche con guscio e l’uso del confezionamento in atmosfera protettiva (MAP) potrebbe risultare una valida alternativa per il mantenimento delle caratteristiche qualitative dell’uovo durante la conservazione. Studi precedenti dimostrano come l’utilizzo di MAP con elevati livelli di CO2 risulti benefico per mantenere delle caratteristiche complessive dell’uovo ma l’utilizzo di materiali di imballaggio ad alta barriera, necessari per mantenere una certa concentrazione di CO2, può provocare l’aumento dell’umidità nello spazio di testa, con conseguenti problematiche legate allo sviluppo microbico sul guscio del prodotto possibilmente risolvibile con l’uso di imballaggi attivi dotati di assorbitori di umidità. Un alternativa, può essere l’utilizzo congiunto di trattamenti di decontaminazione e di confezionamento in MAP. Premesso questo, l’obiettivo di questa ricerca è stato quello di valutare l’effetto congiunto del trattamento di decontaminazione con UV e di confezionamento in atmosfera modificata su alcune caratteristiche qualitative ed igienico sanitarie di uova fresche con guscio confezionate in MAP al 100% di CO2 e in aria durante 28 giorni di conservazione a 21°C. Nella seconda fase della sperimentazione sono stati valutati gli effetti delle differenti modalità di imballaggio su alcune caratteristiche qualitative di pasta all’uovo (tagliatelle). Sono stati realizzati campioni di pasta fresca (utilizzando le uova trattate) sui quali sono state valutate alcune caratteristiche qualitative prima e dopo cottura, confrontate con quelle di pasta ottenuta con uova non trattate.

Preparazione e proprietà di trasporto di gas di membrane a base di polimeri e nanoplatelets grafenici per la cattura di CO2 da processi energetici

Lo scopo di questo studio sperimentale è stato quello di determinare l’effetto dell’aggiunta di piccole quantità (1wt%) di grafene e ossido di grafene al poli(1-trimetilsilil-1-propino) (PTMSP). Il PTMSP è uno dei polimeri più promettenti per la separazione di gas tramite membrane polimeriche grazie al suo elevato volume libero (26%). Sono state studiate sia membrane spesse (60-180 micron) preparate per solvent casting che sottili (2-10 micron) preparate per spin coating supportate su un film poroso di polipropilene commerciale. L’ossido di grafene aumenta la permeabilità del PTMSP, mentre il grafene ha mostrato un comportamento variabile in funzione del protocollo di preparazione che è risultato dipendere fortemente dalla velocità di evaporazione del solvente. Le membrane così ottenute sono state testate al permeometro. È stata osservata una dipendenza della permeabilità in funzione dello spessore del film e del grado di invecchiamento. In particolare, la presenza di nanofiller riduce il grado di invecchiamento dei film di PTMSP. Nel caso specifico della coppia di gas permeanti He/CO2, i campioni hanno mostrato un comportamento intercambiabile di selettività all’He o alla CO2, modulabile in funzione della temperatura tra 30-60°C e del filler utilizzato.

Sviluppo di una fascia addominale per angiografia con CO2

La scelta del mezzo di contrasto in angiografia è rilevante e richiede un’attenta valutazione della qualità diagnostica delle immagini e degli effetti collaterali. Essenziale è analizzare il rischio che comporta l’utilizzo dei vari mezzi di contrasto a base di iodio, come ad esempio la nefropatia. Al contrario l’anidride carbonica, riconosciuta come unico agente di contrasto sicuro, sempre più, viene utilizzata in tutti i vasi del corpo al di sotto del diaframma. L'obiettivo principale di questo lavoro, svolto in collaborazione con l’azienda bolognese Angiodroid srl, è quello di realizzare un dispositivo medico in grado migliorare la qualità delle immagini ottenute con CO2 a livello addominale. Infatti, col recente utilizzo della CO2 anche nel distretto addominale si riduce drasticamente l’utilizzo di grandi quantità di iodio, ma, in molti pazienti, il movimento della aria intestinale che ha coefficiente di assorbimento simile all’anidride carbonica, rende l’immagine inefficiente. Il progetto consiste in una fascia addominale composta da tre camere d’aria gonfiabili manualmente, che comprimendo l’addome con pressioni di 120-180 mmHg, spostano l’aria e riducono il movimento intestinale, e quindi gli artefatti. L’uso di questa semplice fascia, migliorando le immagini dei distretti addominale e viscerale, potrebbe permettere una più rapida affermazione dell’angiografia con CO2 anche in procedure come EVAR e PTA iliache. Per individuare la procedura d’utilizzo più adeguata e migliorare il dispositivo secondo le necessità cliniche, la fascia è stata provata in alcune sale angiografiche dell’Emilia Romagna, Lombardia e Campania.