1,2-dichloroethane (1,2-DCA) is a popular industrial chlorinated organic chemical. Because 1,2-DCA is a dense non-aqueous phase liquid and easily accumulated in deep soil and water, it is difficult to be removed from the contaminated sites. In this study, aerobic and anaerobic microcosm batch experiments were performed to evaluate the feasibility of biodegradation of 1,2-DCA by adding different growth substrates. The aerobic microcosm results show that approximately 90% of 1,2-DCA removal was observed in the natural degradation group (A1) and the aerobic sludge addition group (A3) after 7 days of incubation. Up to 95% of 1,2-DCA removal could be observed in the substrate supplement group in after 14 days of incubation. In the anaerobic microcosm studies, 50% of 1,2-DCA removal could be obtained in all groups after 10 days except for the natural degradation group (B1). Moreover, the degradation efficiency for the anaerobic sludge group (B3) reached 80% of 1,2-DCA removal in 5 days. The DGGE profiles show that the microbial diversity varied with time and the sugar supplement groups (A2, B2) exhibited the most microbial diversity. Bacterial clones results revealed that the 1,2-DCA biodegradable microbial strains were presented in the microcosms, such as Klebsiella, Pseudomonas, Rhodoferax and Xanthobactor. The real-time PCR results indicated that the Dehalococcoides spp. was the major bacterium that was responsible for the degradation of 1,2-DCA in the anaerobic substrate supplement group (B2). Desulfitobacterium spp. could be the dominant 1,2-DCA degrading bacterium for the aerobic substrate supplement group (A2) and all of the anaerobic groups (B1, B2, B3, B4).

The aim of this study was to access the efficacy of an enhanced in situ bioremediation technology at a 1,2-dichloroethane (1,2-DCA) polluted site in southern Taiwan. A water-soluble substrate was injected into the groundwater to provide carbon sources for microbial growth. After substrate injection, increased total organic carbon (TOC) concentrations and microbial populations including Dehalococcoides spp. and Desulfitobacterium spp. were observed in the groundwater. Microbial diversity was analyzed using denaturing gradient gel electrophoresis (DGGE) and 16S rDNA sequencing to identify the bacterial strains. The results showed that after 4.5 months of substrate injection, the reduction-oxidation potential (ORP) changed from aerobic to anaerobic conditions. The less oxygen-tolerable 1,2-DCA degrading bacteria Dehalococcoides spp. started to accumulate in groundwater. However, the more oxygen-tolerable Desulfitobacterium spp. didn¡¦t show a prominent change, although the ORP was suitable for Desulfitobacterium spp. to carry out reductive dechlorination. The DGGE results indicate that with the injected carbon sources and mineral nutrients, both the groundwater microbial diversity and the amount of dominant bacteria were increased. The 16S rDNA sequencing demonstrated that the amount and diversity of 1,2-DCA degradation-related bacteria also increased with the injection of substrate. Six groups of 1,2-DCA degradation related reactions were found: dechlorination, chlorinated-compound degradation, denitrification, iron-reduction, sulfate-reduction and methane-utilizing. Four species that can directly degrade 1,2-DCA were found: Dehalobacter sp., Dehalococcoides sp., Nitrosospira sp. and Pseudomonas sp. Moreover, 11 methane-utilizing bacterial species were also discovered. The presence of these methane-utilizing bacteria not only might assist the process of denitrification and sulfate-reduction, but also could diminish the emission of the greenhouse gas. The results of this study confirmed that the addition of substrates could affect the groundwater oxidation-reduction state and enhance the bioremediation at the 1,2-DCA-contaminated site. Thus, enhanced in situ bioremediation is a feasible technology for site remediation.

Biopile and landfarming systems are ex situ technologies developed for the remediation of contaminated soils. In this study, laboratory degradation experiments and a combined full-scale landfarming and biopile system were operated for the remediation of diesel fuel-contaminated soils. The effectiveness of bulking agents (wood chips and rice hulls), inorganic nutrients (N and P), and biological agent on petroleum hydrocarbon biodegradation were also evaluated. The ratios of contaminated soils to bulking agents applied in the experiments were 1:0, 3:1, 6:1, and 10:1. The soil to bulking agent ratio of 10.7:1 was applied in the full-scale system. After 93 days of incubation, the highest reduction rate for total petroleum hydrocarbon - diesel (TPHd) removal was observed in the experiment with a soil to bulking agent ratio of 3:1. Results show that TPHd degradation trend followed a typical first-order degradation pattern. The calculated regression coefficient ranged from 0.008 ¡V 0.0129. Results also indicate that the addition of biological agent had a significant enhancement of TPHd removal. Results from the full-scale study show that the average TPHd concentrations from 5,544 mg/kg to 488 mg/kg after 231 days of operation. This implies that approximately 91.2% of TPHd removal was obtained. Field results show that temperature affected biodegradation rates, production of CO2, total hererotrophic bacterial biomass, and TPHd reduction efficiencies. Thus, temperature plays an important role for the operation of is biopile and landfarming systems.

In this field-scale study, air sparging (AS) system was applied at a petroleum-hydrocarbon spill site to remediate contaminated soil and groundwater in situ. The objective of this study was to evaluate the effectiveness of the AS system on volatile organic compounds (VOC) removal via the volatilization mechanism. Moreover, the AS system would also enhance the in situ bioremediation process due to the increased oxygen concentration in the subsurface. Results from the preliminary site characterization show that high concentrations of benzene and toluene were present in the subsurface in the western part of the site. Up to 15.62 and 30,957 mg/Kg of benzene and toluene were detected in soil samples, respectively. Moreover, up to 0.068 and 4.8 mg/L of benzene and toluene were observed in groundwater samples, respectively. The following remediation activities were conducted during the one-year investigation and remediation period: 1. Construction of four recovery wells were for light non-aqueous phase liquid (LNAPL) and contaminated groundwater extraction to prevent the expansion of VOC plume. The extracted groundwater was delivered to the wastewater treatment plant for treatment before discharge. 2. Installation of ten air sparging wells to enhance the removal of VOC through volatilization and biodegradation processes. 3. Conduction of (1) soil gas survey, (2) soil and groundwater sampling and analyses, and microbial enumeration periodically to evaluate the effectiveness of AS on VOC removal. Results from the field-scale study indicate that the AS system is able to effectively contain the plume. This can be confirmed by the following findings: (1) decrease in VOC concentrations in both soil and groundwater, (2) increase in carbon dioxide and increase in oxygen concentrations in the soil gas samples, and (3) increase in bacterial population in soil samples. Results from this study indicate that AS system can effectively contain the plume and manage this petroleum hydrocarbon spill site.

Abstract The industrial solvents tetrachloroethylene (PCE) and trichloroethylene (TCE) are among the most ubiquitous chlorinated compounds found in groundwater contamination. One potential method for managing PCE/TCE contaminated sites is the intrinsic bioremediation. Recent regulations adopted by U.S. Environmental Protection Agency allow intrinsic bioremediation to be considered as an alternative during development of corrective action plans. In some remediation cases, enhanced bioremediation are performed to accelerate the contaminant biodegradation rate. The main objective of this study was to evaluate the potential of using intrinsic and enhanced bioremediation technologies to clean up PCE/TCE contaminated aquifers. PCE/TCE bioavailability was evaluated by laboratory microcosms under four reduction/oxidation (redox) conditions including aerobic cometabolism, methanogenesis, iron reduction, and reductive dechlorination. Acclimated bacteria, activated sludge, and aquifer sediments from a pentachlorophenol contaminated site were used as the inocula in this study. Methane, toluene, phenol, sludge cake, and cane molasses were used as the primary substrates (carbon sources) in the cometabolism and reductive dechlorination microcosms. Results from this study show that PCE and TCE can be significantly biodegraded under reductive dechlorination and aerobic cometabolism conditions, respectively. All five carbon sources evaluated in this study can be applied as the primary substrates by microbial consortia to enhance the aerobic cometabolism of TCE. The highest TCE degradation rate [Up to 100% of TCE removal (with an initial concentration of 3.6µM)] was observed in the microcosms with toluene enrichment bacteria as the microbial inocula and toluene as the primary substrate. Under reductive dechlorination conditions, both sludge cake and cane molasses could be used as the primary substrates by microbial consortia (from activated sludge and aquifer sediments) and enhanced the biodegradation of PCE. The highest PCE degradation rate [Up to 100% of PCE removal (with an initial concentration of 17µM)] was observed in the microcosms with anaerobic activated sludge as the microbial inocula and sludge cake as the primary substrate. Except for reductive dechlorination microcosms, no significant PCE removal was observed in the microcosms prepared under iron reduction conditions. Results from this feasibility study would be useful in designing a scale-up in situ (e.g., in situ biobarrier system) or on-site bioremediation system (e.g., bioslurry reactor) for field application. Moreover, the application of non-toxic organic waste to enhance PCE/TCE biodegradation has the potential to become an environmentally and economically acceptable technology for the bioremediation of chlorinated-solvent contaminated groundwater.

This research was initiated after a 100-year flood caused an oil spill on the San Jacinto River (Houston, Texas) in October of 1994. After the floodwaters subsided the released petroleum floating on the water was deposited on the surrounding lands. The petroleum spill was used as an opportunity to research intrinsic petroleum biodegradation in a 9-acre petroleum impacted estuarine wetland. The first phase of this research (Phase I) began in December 1994, approximately 1.5 months after the spill of opportunity and involved the study and quantification of in-situ petroleum biodegradation. The second phase of the research (Phase II) began in March 1996 with a controlled oil release to study and evaluate the success of two bioremediation treatments versus natural biodegradation. The study of in-situ petroleum hydrocarbon degradation and the evaluation of bioremediation amendments were successfully quantified using GC-MS analytical techniques. However, the GC-MS technique is limited to the analyses of hydrocarbon compounds, a disadvantage that precludes the overall characterization of petroleum degradation. The research presented here details an analytical technique that was used to provide a full characterization of temporal petroleum biodegradation. This technique uses thin layer chromatography coupled with flame ionization detection (TLC-FID) to characterize the saturate and aromatic (hydrocarbon) fractions and the resin and asphaltene (non-hydrocarbon, polar) fractions. Other analysis techniques, such as HPLC-SARA analysis, are available for the full characterization of the four petroleum fractions. However, these techniques do not lend themselves well to the application of large sample set analysis. A significant advantage of the TLC-FID analysis to other petroleum analysis techniques is the ability to analyze several samples concurrently and quickly with relative ease and few resources. For the purposes of the Phase I and Phase II research the TLC-FID analysis method was evaluated, refined and applied to quantify the temporal biodegradation and bioremediation of petroleum. While the TLC-FID analysis produces a full characterization, it cannot supplant the GC-MS analysis for petroleum bioremediation research. However, it can be used in conjunction with the GC-MS to expand the knowledge of petroleum bioremediation and remediation strategies.

Toxic waste disposal problems have become enormous due to the proliferation of xenobiotic compounds for use in agricultural, industrial and numerous other applications. Organophosphate (OP) pesticides are commonly used in agriculture and their toxicity is associated with inhibition of cholinesterase in the exposed organism. Some OPs have been shown to produce OP-induced delayed neuropathy (OPIDN). The overall goal of the work described in this thesis was to develop bacterial consortia to remediate hazardous substances at significantly higher rates than found with natural systems. Specifically, degradation of methyl parathion (MP) by hydrolysis with a genetically engineered Escherichia coli was investigated along with degradation of one of the resulting products, p-nitrophenol (PNP), by Sphingobium chlorophenolicum ATCC 53874. Simultaneous degradation of both MP and PNP was investigated using a consortium of a genetically engineered Escherichia coli and a native S. chlorophenolicum. Concentrations of MP and PNP were measured by high performance liquid chromatography (HPLC). Non-growing freely suspended recombinant OPH+ E. coli cells efficiently degraded MP without addition of nutrients for growth. Maximum reactor productivity was found with a biomass concentration of 25 g/L. Substrate inhibition did not occur up to 3 g MP/L. The simple Michaelis-Menten kinetic model for enzymatic reactions provided a good fit of the degradation data with Vm=11.45 ??mol/min??g-biomass and Km=2.73 g/L. B. cepacia failed to degrade PNP under the experimental conditions evaluated, so further studies were not conducted. Growing cultures of S. chlorophenolicum degraded PNP at concentrations up to 0.1 g/L without a lag phase in mineral salts glutamate medium. Parameters such as initial pH, growth medium and growth stage for addition of PNP were important degradation factors. The bacterium exhibited substantial growth in the degradation process. Hydroquinone (HQ) or nitrocatechol (NC) were not identified as products of PNP degradation. The recombinant OPH+ E. coli and S. chlorophenolicum consortium failed to degrade PNP when starting with higher concentrations of MP. The presence of organic solvent in the bacterial consortium degradation medium negatively affected the degradation of PNP. The genetically engineered organism efficiently degraded high concentrations of MP, but the resulting high concentration of intermediate product (PNP) inhibited growth of the native type organism. Biodegradation by consortia of genetically engineered non-growing and native-type organisms generally will be limited by the growing native-type organism.

Thesis (M.S.)--Bowling Green State University, 2009. / Document formatted into pages; contains viii, 38 p. : ill. Includes bibliographical references.

Thesis (M.S.)--Youngstown State University, 2009. / Includes bibliographical references (leaves 38-42). Also available via the World Wide Web in PDF format.

Thesis (Ph. D.)--Rutgers University, 2009. / "Graduate Program in Microbiology and Molecular Genetics." Includes bibliographical references (p. 112-131).