The regioselectivity of the reaction of hydroxyl radical addition to toluene and naphthalene are examined in this study over the temperature range of 25°C-45°C. Also, the relative rates of reactivity as compared to benzene are determined for toluene, naphthalene, mesitylene, and p-xylene over the same temperature range. 2-(t-Butylazo)prop-2-yl hydroperoxide was used as the hydroxyl radical source and 1,1,3,3-tetramethylisoindolin-2-yloxyl was used as radical trap. For toluene the relative rates of addition were found to be 4 times greater for the ortho position versus the meta postion and 2 times greater for the para position versus the meta position, when the number of meta and para sites are taken into account. / Department of Chemistry

No description available.

No description available.

No description available.

1 / Yue Sun

Two case studies are described where partially biodegraded petroleum residues were collected from the marine environment and analysed to investigate the changes in aromatic hydrocarbons with increasing biodegradation.The first of these studies, involved following the weathering of sea-floor residues from drilling discharges from an offshore petroleum exploration and production platform situated off the coast of North Western Australia. During operations, formation cuttings with adhering oil-based drilling muds were discharged into the ocean via a chute into approximately 125n1 of water, forming a substantial mound at the base of the platform. A suite of seabed sediments was collected from 16 sampling sites at various distances from the platform immediately following the cessation of drilling operations. The distribution of hydrocarbons in the sediment directly under tile cuttings chute was consistent with that found in drilling fluids formulated from a kerosene-like fluid. The samples from more remote sites exhibited the successive enhancement of an unresolved complex mixture relative to the n-alkanes, associated with tile presence of residues from petroleum biodegradation processes. In a subsequent sampling some three years later, a 10 cm core was retrieved from the cuttings pile and divided into 1 cm depth intervals. Samples within 6 cm of the surface of the cuttings pile contained biodegraded residues of the drilling mud, where the extent of biodegradation increased with decreasing proximity to the surface, most likely indicative of aerobic biodegradation. Biodegradation was less evident in the underlying sediments, where anaerobic conditions prevailed. / Analysis of the aromatic hydrocarbons in both sets of sediment extracts by using gas chromatography-mass spectrometry (GC-MS) revealed the successive depletion of alkylnaphthalenes, and due to the subtlety of changes in the extent of biodegradation, provided an excellent opportunity to examine the susceptibility of biodegradation towards the individual alkylnaphthalenes in the marine environment. Conventional GC-MS analysis of these mixtures is performed under chromatographic conditions where complete resolution of the mixture is not achieved and several isomers co-elute. The mass spectra of these co-eluting isomers may be so similar that one is unable to differentiate between them, and their abundance may therefore not be determined. Since each isomer has a unique infrared spectrum, however, the abundance of each individual isomer was determined by comparing the infrared spectrum of the co-eluting compounds with the spectrum of each of the isomers. To this end, techniques were developed for the application of direct-deposition gas chromatography - Fourier transform infrared spectroscopy (GCFTIR) to the analysis of the complex mixture of alkylnaphthalenes present in the petroleum. This technique was also extended to discriminate between individual alkylphenanthrene isomers, and to clarify the sorption behaviour of the dimethylphenanthrenes by mordenite molecular sieves. The identification of other compounds of geochemical significance in petroleum is also described. / Analyses of' the aromatic hydrocarbons in the contaminated sea-floor sediments using GC-FTIR enabled the unambiguous identification and quantification of each of the dimethylnaphthalene, trimethylnaphthalene and tetramethylnaphthalene isomers present in the samples, from which the relative extents of depletion of each with increasing extent of biodegradation were determined. It was apparent from the considerable differences in the observed susceptibility to biodegradation that a strong relationship exists between the compound structure and its susceptibility to biodegradation, with 1,6-disubstituted polymethylnaphthalenes being preferentially depleted relative to other isomers that lack this feature. The second case study involved tracking the fate (weathering) of hydrocarbons from an accidental release of condensate from a buried pipeline into intertidal coastal (mangrove) sediments in North Western Australia. Sediment samples were collected on nine occasions over a three-year period. Chemical analysis of the saturated and aromatic hydrocarbon components of the petroleum extracts revealed that both hydrocarbon fractions exhibited an increasingly biodegraded profile with increased residence time in the sediments. In a similar manner to the first case study, detailed analysis of the aromatic hydrocarbons using GC-FTIR techniques was performed to determine the depletion of individual alkylnaphthalene isomers with increasing extent of biodegradation. It was apparent that a relationship similar to that observed for the sea-floor sediments exists between the alkylnaphthalene structure and its susceptibility to biodegradation. / Changes in the distribution of methylphenanthrene and dimethylphenanthrene isomer mixtures were also studied and the susceptibility to biodegradation amongst these determined in a similar manner. These relative susceptibilities to biodegradation of the aromatic hydrocarbons were then related to the established hierarchy of susceptibilities of the saturated hydrocarbons, in effect providing a second parallel system for the assessment of the extent of biodegradation. Finally, a system of ratios calculated from the relative abundances of selected aromatic hydrocarbons was developed and used as indicators to differentiate between several crude oils that have been biodegraded to varying extents. These parameters also offer promise as indicators of multiple accumulation events in oil reservoirs where petroleum fluids biodegraded to differing extents are mixed.

Thesis (Ph. D.)--Oregon State University, 2007. / Printout. Includes bibliographical references. Also available on the World Wide Web.

Polycyclic aromatic hydrocarbons (PAHs) are environmentally significant compounds due to the toxicity of some members. They are ubiquitous and are persistent bioaccumulative toxins(PBTs). The toxicity of PAHs represents a risk to human health, and there are varied risk assessment approaches to quantifying the risk posed by PAHs based on exposure routes and scenarios. PAHs are not carcinogenic until they are metabolically activated as the body attempts to break them down and forms reactive metabolites that bind to the DNA causing subsequent replication in the cells. Fundamental to assessing the risk posed by PAHs is understanding the metabolism of PAHs. Since exposure to PAHs is never to single PAHs, understanding what differences may occur in mixtures of PAHs gives accurate assessment of the dangers of PAHs. Understanding the dynamics of complex metabolism vis-a-vis single metabolism of PAHs and possible effects on the toxicity expression of PAHs is a necessary advancement to accurately impact and guide remediation strategies. Studies were carried out comparing the metabolism of the PAHs Phenanthrene (PHE), Flouranthene (FLA) and Benzo[a]pyrene (BAP) in single, binary and ternary mixtures by monitoring the disappearance of the parent compound. It was observed that PAH metabolism in the single PAH experiment differed from metabolism in both binary and ternary mixtures. Enzyme competition was evident in the metabolism of mixtures, changing significantly the metabolism patterns of individual PAHs. PAH structure was also seen to affect metabolism in mixtures and the possible creation of toxicity effects during mixture metabolism. PAH concentration changed over time with faster change during single PAH metabolism followed by ternary mixture metabolism and finally binary metabolism. These results affirm that substrate interactions must be considered in the risk assessment approaches to the dangers posed by exposure to PAHs.

Polycyclic aromatic hydrocarbons (PAH) have been identified as a serious environmental problem. In past research it has been proven that naphthalene, the simplest PAH, could be biodegraded using roller bioreactors and Pseudomonas putida. In this previous work it became apparent that the mass transfer rate of the hydrophobic naphthalene was the rate limiting factor in biodegradation, as the bacteria could degrade the naphthalene as fast as it entered solution. The challenge for the present research was to find a simple, inexpensive method for increasing the mass transfer rates within the framework of the previously successful reactor. <p>After some deliberation, the addition of inert particles (glass beads) was determined to be the preferred option to increase mass transfer. The inert particles visibly increased the turbulence in the reactor and significant increases in both mass transfer and bioremediation rates were achieved. The augmentation of mass transfer rates was found to be dependent on the type, size and relative loading of the particles. Two types of inert particles were investigated to increase mass transfer rates, spherical glass beads and Raschig rings. Glass beads were found to be far superior to Raschig rings for the intended purpose. Three sizes of spherical glass beads were then compared experimentally (1, 3, and 5mm). It was discovered that the 3mm beads were vastly superior to 1mm beads and 5 mm beads were slightly superior to 3mm beads. Different bead loadings (volume of particles / total working volume) were then explored with 10%, 25% and 50% bead loading investigated. Although slight increases in mass transfer were observed at higher bead loadings, the reduction in working volume for biodegradation meant that 50% was accepted as the optimum loading parameter. <p>The optimum conditions for maximum mass transfer occurred using 5 mm spherical glass beads at 50% loading. The increase in mass transfer and biodegradation rates compared to a traditional roller bioreactor were found to be 10 fold and 11 fold, respectively. The optimum mass transfer conditions were then applied to 2-methylnaphthalene with increases in mass transfer and biodegradation equal to 6 fold and 8 fold, respectively. The candidate bacteria used in this study was found incapable of degrading 1,5 dimethylnaphthalene although the mass transfer results demonstrate promise for the developed technology. To determine the effects of scale on the process, two larger reactors were finally studied. They were eight times and twenty-one times the size of the initial bioreactor. The process was shown to speed up at larger scale which shows great promise for future applications. The maximum degradation rate achieved in the larger reactor was 148 mgL-1h-1. This compares very well with the best result found in literature, 119 mgL-1h-1, which was achieved in a much more complex system. Clearly, the bead mill bioreactor designed during the present work is a simple concept that shows superior performance for the bioremediation of PAHs.

Polycyclic aromatic hydrocarbons (PAHs) and metals are co-contaminants of aquatic environments near industrial and urbanized areas. Mixtures could result in synergistic toxicity impairing macrophyte growth and potentially causing bioaccumulation and biomagnification throughout the ecosystem. In this study, combinations of 1,2-dihydroxyanthraquinone (1,2-dhATQ) and copper (Cu) at low concentrations synergistically inhibited Lemna gibba (duckweed) growth. Further analysis using fluorescence techniques showed an increase in reactive oxygen species (ROS) levels upon Cu exposures possibly through redox cycling in the chloroplasts. Pulse amplitude modulated (PAM) and fast repetition rate fluorometry (FRRF) indicated that plants exposed to 1,2-dhATQ had impaired photosynthetic electron transport that manifested as a decrease in the yield of photosynthesis and change in the redox status of the plastoquinone (PQ) pool. At the gene expression level acetyl coA carboxylase (ACC), a key enzyme in membrane repair, and serine decarboxylase (SDC), another enzyme needed for membrane repair were up-regulated in response to copper and 1,2-dhATQ, respectively. The mechanism for mixtures toxicity is thought to involve the reduced PQ pool which could serve as a source of electrons for copper redox cycling thereby increasing ROS production and causing synergistic growth inhibition. When the antioxidant glutathione (GSH) was added, copper toxicity was ameliorated but 1,2-dhATQ toxicity increased possibly through formation of reactive conjugates or suppression of the native antioxidant system. This study emphasizes that mixtures of toxicants at low concentrations can cause more biological damage than individual toxicants via alterations of the redox status and increases in ROS production.