<p>The shallow soils of a former orchard area in Point Pelee National Park, near Leamington, Ontario, Canada have elevated concentrations of chlorinated pesticides above the regulatory limits. Previous studies in this area have shown that the DDT, DOE and ODD are highly persistent with an estimated half-life of DDT in the range of 15-30 years. In 2002 a pilot-scale field remediation experiment involving the application of cyclodextrin was conducted. This experiment resulted in substantial decrease of DDT, DDE and DDD concentrations in the upper soil layer within the remediation grid. Soil samples were collected within the treatment plots a year after the cyclodextrin application was completed to assess any further changes in concentrations of DDT, DDE and DDD. Groundwater samples were collected in the vicinity of the soil remediation grid which provided DDT, DDE and DDD concentrations in groundwater to assess the vertical mobilization of the compounds. Mass balance of the "soil - groundwater" system was calculated in order to estimate the degradation rate of DDT within the remediation zone. The 2-D unsaturated/saturated flow and solute transport numerical model "HYDRUS 2-D" was used to gain a better estimation of DDT, DDE and DDD mass and distribution in groundwater. The effectiveness of cyclodextrin application for remediation of DDT contaminated soils was assessed. After remediation treatments had stopped, there was no indication of further degradation of DDT and its metabolites in the upper layer of soil. The groundwater concentration of DDT, DDE and DDD near the remediation grid was 10-100 times higher than background value. This increase in groundwater concentration is a direct indication of DDT, DDE and DDD mobilization by cyclodextrin. The estimates of total mass of DDT in groundwater are less than 1% of mass leached from the soil. It was concluded that the application of cyclodextrin promoted enhanced co-metabolic biodegradation of DDT and it metabolites DDE and DDD. The estimated half-life for the displaced DDT was less than 2 months. This work demonstrates that cyclodextrin can be a highly effective agent for remediation of DDT contaminated soils.<p> / Thesis / Master of Science (MSc)

Significant progress in reducing the growth temperature of the SiC epitaxial growth became possible in the previous work by using new chloro-carbon epitaxial growth method. However, it was established that even in the new process, homogenous nucleation of Si in the gas phase limited the growth rate. In the present work, new chlorinated silicon precursor SiCl4 was investigated as a replacement for the traditional silicon precursor SiH4 during the low-temperature chlorocarbon epitaxial growth. The new process completely eliminated the homogenous nucleation in the gas phase. Growth rate of 5-6 μm/h was achieved at 1300°C compared to less than 3 μm/h in the SiH4-based growth. The growth dependence on the C/Si ratio revealed that the transition from the C-supply-limited to the Si-supply-limited growth mode takes place at the value of the C/Si ratio much higher than unity, suggesting that certain carbon-containing species are favorably excluded from the surface reactions in the new process. Morphology degradation mechanisms, which are unique for the lowtemperature growth, were observed outside the established process window. Prior to this work, it remained unclear if CH3Cl simply served as a source of Cl to suppress homogeneous nucleation in the gas phase, or if it brought some other unknown improvements. In this work true benefits of CH3Cl in providing unique improvement mechanisms have been revealed. It was established that CH3Cl provided a much wider process window compared to C3H8. In contrast, even a very significant supply of extra Cl from a chlorinated silicon precursor or from HCl during the C3H8-based growth could not provide a similar benefit. The combination of the chloro-carbon and the chloro-silane precursors was also investigated at conventional growth temperature. High-quality thick epitaxial layers, with the growth rate up to 100μm/h were obtained, and the factors influencing the growth rate and morphology were investigated. Extensive optical and electrical characterization of the low-temperature and the regular-temperature epitaxial layers was conducted. The device-quality of the lowtemperature chloro-carbon epilayers was validated for the first time since the development of the chloro-carbon epitaxial process in the year 2005 by fabricating simple Schottky diodes and investigating their electrical characteristics.

No description available.

No description available.

No / Originally developed as a heat exchange fluid, Volasil 245 (decamethylcyclopentasiloxane) has been found to dissolve 10 times more ozone than water does. This article proposes and investigates the extraction of wastewater contaminants to ozone-loaded Volasil 245 as a means of providing rapid treatment. In a series of bench-scale tests, the effectiveness of ozone-loaded Volasil 245 contact was compared with that of conventional gas contact. Tests were conducted with respect to a range of organic compounds: namely, phenol, 2-chlorophenol, 2,3-dichlorophenol, 1,3-dichlorobenzene, o-nitrotoluene, and nitrobenzene. Contact with the ozone-loaded solvent was suggested to be the more rapid technique, reducing aqueous concentrations by at least 85% within 30 s. In the case of 2-chlorophenol, Volasil 245 contact was shown to require just ~0.5 min to achieve a residual aqueous fraction of 5%, as opposed to ~4.5 min of gas contact. However, water/solvent interfacial mass transfer resistance was suggested to limit the degree of aqueous decontamination ultimately achieved.

For a numerical or analytical model to be useful it should be ensured that the model outcome matches the observations or field measurements during calibration. This process has been typically done by manual perturbation of the model input parameters. This research investigates a methodology for using non linear parameter estimation technique (the Marquardt-Levenberg technique) with the multi component reactive solute transport model SEAM3D. The reactive multi-component solutes considered in this study are chlorinated ethenes. Previous studies have shown that this class of compounds can be degraded by four different biodegradation mechanisms, and the degradation path is a function of the prevailing oxidation reduction conditions. Tests were performed in three levels; the first level utilized synthetic model-generated data. The idea was to develop a methodology and perform preliminary testing where "observations" can be generated as needed. The second level of testing involved performing the testing on a single redox zone model. The methodology was refined and tested using data from a chlorinated ethenes-contaminated site. The third level involved performing the tests on a multiple redox zone model. The methodology was tested, and statistical validation of the recommended methodology was performed. The results of the tests showed that there is a statistical advantage for choosing a subgroup of the available parameters to optimize instead of the optimizing the whole available group. Therefore, it is recommended to perform a parameter sensitivity study prior to the optimization process to identify the suitable parameters to be chosen. The methodology suggests optimizing the oxidation-reduction species parameters first then calibrating the chlorinated ethenes model. The results of the tests also proved the advantage of the sequential optimization of the model parameters, therefore the parameters of the parent compound are optimized, updated in the daughter compound model, for which the parameters are then optimized so on. The test results suggested considering the concentrations of the daughter compounds when optimizing the parameters of the parent compounds. As for the observation weights, the tests suggest starting the applied observation weights during the optimization process at values of one and changing them if needed. Overall the proposed methodology proved to be very efficient. The optimization methodology yielded sets of model parameters capable of generating concentration profiles with great resemblance to the observed concentration profiles in the two chlorinated ethenes site models considered. / Ph. D.

Chlorinated ethenes are considered one of the most prevalent sources of groundwater contamination in developed countries. Natural attenuation of chlorinated ethenes is possible through the process of microbial reductive dechlorination. Reductive dechlorination can occur in contaminated aquifers where there are sufficient amounts of organic carbon and reducing redox conditions to support dechlorinating microorganisms. Natural organic carbon (NOC) from dissolved aquifer sediment is thought to be the source of fermentable compounds needed to produce molecular hydrogen that functions as the primary electron donor for reductive dechlorination. Therefore, in an anaerobic aquifer, the production of molecular hydrogen from the fermentation of NOC drives the reductive dechlorination process. The variability and distribution of potential bioavailable organic carbon (PBOC) at a site is relatively unknown and any potential relationships between PBOC and the physical properties of the aquifer sediment have not been evaluated. Exploring relationships between the grain size of aquifer sediment PBOC may help to determine the feasibility of natural attenuation as a long-term remediation strategy at chlorinated ethene-contaminated sites. Because hydraulic conductivity is directly related to aquifer sediment grain size, zones of high hydraulic conductivity may promote greater microbial activity or biodegradation because of the increased availability of PBOC and nutrient flux. To determine potential relationships between PBOC and aquifer sediment grain size, two experiments were performed. PBOC was measured for 106 sediment samples impacted by chlorinated solvent contamination from an anaerobic type II site through a multiple liquid extraction process (Rectanus et al. 2007). Grain size distributions for each of the 106 sediment samples were determined by conducting sieve analyses. The results of both experiments were compared to explore relationships between PBOC and sediment grain size and to evaluate spatial distribution of both in the surficial aquifer. / Master of Science

The feasibility of applying a recently developed liquid-liquid extraction method termed Predispersed Solvent Extraction (PDSE) in an <i>ex situ</i> pump-and-treat system to remove trace amounts of dissolved chlorinated solvents like perchloroethylene (PCE) and trichloroethylene (TCE) from contaminated ground water has been investigated. In PDSE, the solvent is comminuted into globules with diameters ranging from submicron to 100 microns, and stabilized by a surfactant film prior to contact with the aqueous feed. These stabilized globules, termed oil-core aphrons (OCAs), disperse readily in water since water is the continuous phase in systems where the oil-water phase ratios can be as high as 9. Due to their fine particle size and large surface area, high extraction mass-transfer rates are achieved with minimal mixing. OCA phase separation from water can be expedited with microbubble foam flotation. Experiments in this investigation focused on PDSE process development for this groundwater remediation application. Distribution coefficients for PCE and TCE in possible OCA solvents were determined experimentally and agree with published calculated values. Various surfactant/solvent OCA formulations using the aforementioned solvents were examined with emphasis on creating a weakly stable dispersion which would maximize extraction efficiency yet destabilize sufficiently to permit rapid flotation with minimum losses in the raffinate. Accelerating phase separation, hence solvent recovery, through dispersion chemical destabilization with salts, coagulants, and flocculants at varied pH was examined with and without microbubble flotation. The presence of OCAs in the aqueous phase reduced vapor phase concentrations of PCE as much as 96% and was assessed through apparent Henry's Law constants. TCE concentrated in dodecane OCA extract was degraded with a CO-dehydrogenase enzyme complex to cis 1,2-dichloroethylene, trans 1,2-dichloroethylene, and 1,1-dichloroethylene, and vinyl chloride as a possible means of destroying TCE dissolved in the extract. Based on the implications of these experiments, the development of a PDSE <i>ex situ</i> pump-and-treat system appears technically feasible and a conceptual process layout has been provided. / Master of Science

Le potentiel de biodégradation des éthènes chlorés (ECs) et du dichlorométhane (DCM) dans les eaux souterraines de l’ancien site industriel de Themeroil (Varennes-le-Grand, France) a été évalué par des études en microcosmes, à travers l’utilisation de biomarqueurs moléculaires, et par analyse isotopique spécifique au composé (compound specific isotope analysis, CSIA). L’objectif de ce travail a été d’évaluer i) la biodégradation de ces polluants et la diversité bactérienne associée dans les eaux du site, et ii) l’impact de mélanges de contaminants et des conditions rédox dans ce processus. L’implication majeure d’un taxon bactérien affilié à Dehalococcoides dans la dégradation du PCE dans les eaux du site, et son lien potentiel aux gènes de déshalogénase pceA et vcrA associés au processus de déchloration, ont été mises en évidence. La dégradation du DCM en présence d’ECs dans les eaux du site a ensuite été démontrée, et des souches bactériennes dégradant le DCM ont été isolées à partir d’eaux du site et caractérisées. La CSIA a révélé une forte biodégradation du DCM in situ. Des analyses des eaux du site, par qPCR ciblant les gènes dcmA et dhlA de la biodégradation bactérienne du DCM, et par séquençage haut-débit du gène de l’ARNr 16S, ont permis d’évaluer le rôle potentiel de différents taxa bactériens associés à la dégradation du DCM. Il a ainsi été montré que la répartition spatiale de ces taxa sur site dépend dans une large mesure des conditions rédox et du niveau de contamination. L’influence de ces paramètres sur la biodégradation, étudiée ensuite en microcosmes, a été confirmée par l’observation de différents profils de dégradation dans des conditions rédox et de co-contamination distinctes. Ceci suggère la participation de différents types de métabolisme à la biodégradation des éthènes et alcanes chlorés sur site. Les résultats obtenus confirment la pertinence d’études en microcosme pour évaluer le potentiel de biodégradation des polluants halogénés dans les sites contaminés, et pour orienter les traitements de dépollution à privilégier. / The biodegradation potential of chlorinated ethenes (CEs) and dichloromethane (DCM) in groundwater from the former industrial site of Themeroil (Varennes-le-Grand, France) was evaluated in microcosm studies, using molecular biomarkers and compound-specific isotope analysis (CSIA). The objective of this work was to evaluate i) the biodegradation of these pollutants and the associated bacterial diversity in site groundwater, and ii) the impact of contaminant mixtures and redox conditions on biodegradation. The major role of a taxon affiliated to Dehalococcoides in PCE degradation in site groundwater, and its potential link to dehalogenase genes pceA and vcrA associated with the process, were highlighted. Degradation of DCM in the presence of CEs in site groundwater was then demonstrated, and DCM-degrading strains were isolated from site groundwater and characterised. CSIA revealed a large extent of DCM biodegradation in situ. Analyses of groundwater from the site, targeting dcmA and dhlA genes for DCM biodegradation by qPCR, as well as by high-throughput sequencing of the 16S rRNA gene, allowed to evaluate the potential role of different bacterial taxa associated with DCM dehalogenation in DCM degradation on site. It was shown that the spatial distribution of these taxa on site depends significantly from redox conditions and contamination level. The influence of these parameters on biodegradation was also investigated in microcosms, and distinct degradation profiles were observed under different redox and co-contamination conditions. This suggests that different types of metabolism participate in biodegradation of chlorinated ethenes and alkanes on site. Obtained results confirm the relevance of microcosm studies in evaluating halogenated pollutants biodegradation potential on contaminated sites, and in guiding the choice of remediation approaches to be favoured.

Doctor of Philosophy / Department of Chemical Engineering / Larry E. Erickson / Chlorinated solvents are the second most ubiquitous contaminants, next to petroleum hydrocarbons, and many are carcinogens. Tetrachloroethylene or perchloroethene (PCE) has been employed extensively in the dry cleaning industry and carbon tetrachloride (CT) has been used as a fumigant in grain storage facilities. In this work, remediation feasibility studies were conducted by mesocosm experiments; a chamber was divided into six channels and filled with soil, and plants were grown on top. Each channel was fed with contaminated water near the bottom and collected at the outlet, simulating groundwater flow conditions. The contaminants were introduced starting from March 12, 2004. PCE was introduced at a concentration of about 2 mg/L ([similar to]12 [Mu]moles/L) in three channels, two of them with alfalfa plants and the other with grass. CT was introduced at a concentration of about 2 mg/L ([similar to]13 [Mu]moles/L) in the other three channels, two of them with alfalfa plants and the other with grass. After the system had attained steady state, the concentrations of PCE and CT at inlet and outlet were monitored and the amount of PCE and CT disappearing in the saturated zone was studied. Since no degradation products were found at the outlet after about 100 days, one channel-each for PCE and CT (with alfalfa) was made anaerobic by adding one liter of 0.2 % glucose solution. The glucose solution was fed once every month starting from July 1, 2004 and continued until February 2005. From October 1, 2004, one liter of 0.1 % emulsified soy oil methyl esters (SOME) was fed to two other channels (with alfalfa), one exposed to PCE and another exposed to CT. The SOME addition dates were the same as that for glucose. The outlet liquid of the channel fed with PCE and SOME started to contain some of the degradation compounds of PCE; however, the extent of degradation was not as great as that of the glucose fed channel. No degradation compounds were observed in the outlet solution of the channel (grass grown on top) in which no carbon and energy supplements were added. Similar trend was observed in the CT fed channels also. KB-1, a commercially available microbial culture (a consortium of dehalococcoides) that degrades dichloroethene (DCE), was added through the inlet of the PCE fed channels, but this did not lead to sufficient conversion of DCE. Addition of KB-1 at well 3, located approximately in the middle of the channel, had a greater impact in the degradation of DCE, in both glucose and SOME amended channels, compared to addition at the inlet. KB-1 culture added to the channel was active even 155 days later, suggesting that there is sustainable growth of KB-1 when provided with suitable conditions and substrates. A pilot field study was conducted for remediation of a tetrachloroethylene (PCE) contaminated site at Manhattan, KS. The aquifer in the pilot study area has two distinct zones, termed shallow zone and deep zone, with groundwater velocities of about 0.3 m/day and 0.1 m/day. Prior to the pilot study, PCE concentration in groundwater at the pilot study area was about 15 mg/L (ppm) in the deep zone and 1 mg/L in the shallow zone. Nutrient solution comprising soy oil methyl esters (SOME), lactate, yeast extract and glucose was added in the pilot study area for biostimulation, on August 18, 2005. Potassium bromide (KBr) was added to the nutrient solution as a tracer. PCE was converted to DCE under these conditions. To carry out complete degradation of PCE, KB-1, a consortium of Dehalococcoides, and a second dose of nutrient solution were added on October 13, 2005. After addition of KB-1, both PCE and DCE concentrations decreased. Nutrients were again injected on March 3, 2006 (with KBr) and on August 1, 2006. The total chlorinated ethenes (CEs) have decreased by about 80 % in the pilot study area due to bioremediation. Biodegradation of CEs continued for a long time (several months) after the addition of nutrients. The insoluble SOME may be retained at the feeding area and provide a long time source of electron donors. Biostimulation and bioaugmentation of PCE contaminated soil and groundwater was evaluated in the laboratory and this technique was implemented successfully in the pilot field study. Modeling of the tracer study was performed using an advection-dispersion equation (ADE) and traditional residence time distribution (RTD) methods. The dispersion coefficient, groundwater velocity and hydraulic conductivity were estimated from the experimental data. The groundwater velocities vary from 1.5 cm/d to 10 cm/d in the deep zone and 15 cm/d to 40 cm/d in the shallow zone. The velocities estimated from the 2004 tracer study and 2005 tracer study were higher compared to the velocity estimated from the 2006 tracer study, most likely because of microbial growth and product formation that reduced the hydraulic conductivity. Based on data collected from several wells the hydrologic parameter values obtained from tracer studies appear to vary spatially.