In March 1994, a report was issued to the Indiana Department of Environmental Management after Jim Allen Maintenance, Inc. found levels of total petroleum hydrocarbons (TPH) exceeding the level appropriate for action (100 parts per million) during an underground storage tank closure report assessment. Creek Run L.L.C Environmental Engineering was contracted by Jay Petroleum to complete an initial site characterization. Through quarterly monitoring of benzene, toluene, ethyl benzene, and methyl tert-butyl ether for 11 years, Creek Run L.L.C determined that biodegradation was occurring. Upon using BIOSCREEN, a contaminant transport modeling software that simulates natural attenuation over time, it was determined that the retardation factor was 1.4, and the biodegradation rate constant was 4.6 per year. This indicates that the contaminant migration is slow in comparison to groundwater flow, and the rate of biodegradation is at an appropriate value to allow natural attenuation to occur on its own.

Accidental spills of hydrocarbons from underground storage tanks or pipelines are a common cause of subsurface contamination. Anthropogenic hydrocarbon contamination of soil is a global issue throughout the industrialised world. In England and Wales alone, 12% of all serious contamination incidents in 2007 were hydrocarbon related. Biodegradation could be in situ process leading to a decrease of benzene concentrations in groundwater. Recently, monitored natural attenuation has become an effective alternative to the more active remediation methods for the in situ treatment of contaminated subsurface environments. The main objective of this study was to examine the possibility of adopting monitored natural attenuation as a remediation technique for the contaminated groundwater aquifer. In this natural attenuation study, the following tasks were conducted bioremediation investigation, biological first-order decay rates, Mann-Kendall Test model and BIOSCREEN model for the contaminated groundwater aquifer. In this study, a full-scale natural bioremediation investigation was conducted at a petroleum hydrocarbon spill site. In this study, The calculated biodegradation capacity (8.261 mg/L) at this site is much higher than the detected concentrations of petroleum-hydrocarbons (3-4 mg/L) within the most contaminated area inside the plume. Thus, natural biodegradation should be able to remove the contaminants effectively. The calculated biological first-order decay rates for benzene were between 1.7¡Ñ10-3-9.0¡Ñ10-4 day-1 respectively. Mann-Kendall test was applied to analyze the trend of contaminant variations. Results show that the S-value of monitor wells SW-1W, SW-4W, SW-42W, SW-23W, SW-30W, SW-67W and SW-70W were -2.23607, -1.16276, -1.52053, -1.34164, -1.26323, 0 and -1.34164, respectively. The negative S values reveal that the all contaminants tended to decrease. This indicates that the hydrocarbon plume at this site is not expanding, and has been contained effectively by the natural attenuation mechanisms. BIOSCREEN model from the groundwater analyses indicate, a first-order decay model reached the downgradient monitor well located 220 m from the spill location. that approximately 89% of the contaminate removal was due to biodegradation processes. The study of petroleum-hydrocarbons bacterial consortium were include Aquincola tertiaricarbonis L10¡BBosea sp. GR060219¡BBrachymonas petroleovorans strain CHX¡BHydrogenophaga sp. p3(2011)¡BHydrogenophaga sp.¡BMethylibium sp. YIM 61602¡BMycobacterium sp.¡BRhodoferax sp. IMCC1723¡BRhodoferax sp.¡BUncultured Rhodocyclaceae bacterium clone Elev_16S_975¡BUncultured Rhodocyclaceae bacterium clone eub62B1¤ÎUncultured Beggiatoa sp. clone GE7GXPU01BJTWR. Thus, the in situ bioremediation technology has the potential to be developed into an environmentally, economically and naturally acceptable remediation technology. Evidences for the occurrence of natural attenuation include the following: (1) depletion of dissolved oxygen, nitrate, and sulfate; (2) production of dissolved ferrous iron, sulfide, and CO2; (3) decreased BTEX concentrations and BTEX as carbon to TOC ratio along the transport path; (4) increased alkalinity and microbial species; (5) limited spreading of the BTEX plume; and (6) preferential removal of certain BTEX components along the transport path. Results indicate that natural attenuation can effectively contain the plume, and biodegradation processes played an important role on contaminant removal.

Contamination of groundwater by petroleum-hydrocarbons is a widespread environmental problem. Because the petroleum-hydrocarbon resulted plumes could be quite diffuse and widespread, some more economic approaches are desirable for groundwater remediation to provide for long-term control of contaminated groundwater. Monitored natural attenuation (MNA) has been considered as a passive remedial approach to degrade and dissipate contaminants in groundwater. In this study, a full-scale and detailed natural bioremediation investigation was conducted at a petroleum-hydrocarbon spill site in Kaohsiung County, Taiwan. In this natural attenuation study, the following tasks were conducted: (1) groundwater analysis; (2) evaluation of the occurrence of natural attenuation, (3) calculation of biodegradation capacity and natural attenuation rate calculation, (4) evaluation of the percent loss of hydrocarbons due to biodegradation processes by BIOSCREEN model, and (5) application of BIOPLUME III model for the development of remedial strategies. Results show that benzene, toluene, ethylbenzene, and xylene isomers (BTEX) concentrations dropped to below detection limit (BDL) before they reached the downgradient monitor well located 280 m from the spill location. A first-order decay model was applied for the natural attenuation rate calculation. Results reveal that natural biodegradation process was the major cause of the BTEX reduction among the natural attenuation mechanisms. Results from the groundwater analyses indicate that mixed anaerobic biodegradation patterns occurred between the source and mid-plume area, and the aerobic biodegradation dominated the mid and downgradient area. Approximately 74% of the BTEX removal was due to intrinsic biodegradation processes. The calculated natural attenuation rates for BTEX, methyl tert-butyl ether (MTBE), and 1,2,4-trimethylbenzene (1,2,4-TMB) were 0.13, 0.06, and 0.19 1/day, respectively. Evidence for the occurrence of natural attenuation was the decreased contaminant mass flux through the plume cross-sections along the transport path. Evidences for the occurrence of natural BTEX biodegradation included the following: (1) depletion of dissolved oxygen (DO) within the plume; (2) production of biodegradation by-products [Fe(II), CO2, and methane] within the plume; and (3) decreased BTEX concentrations and BTEX as carbon to TOC ratio along the transport path. The calculated biodegradation capacity (45 mg/L) at this site is much higher than the detected concentrations of petroleum-hydrocarbons (1.5 mg/L) within the most contaminated area inside the plume. Thus, natural biodegradation should be able to remove the contaminants effectively. Results suggest that natural attenuation mechanisms can effectively contain the plume and cause the significant removal of petroleum hydrocarbons. Moreover, pump-and-treat and air sparging systems are also feasible technologies to remediate contaminated groundwater at this site.

Methyl tert-butyl ether (MTBE) has been used as a gasoline additive to improve the combustion efficiency and to replace lead since 1978. It is the most commonly used oxygenate now due to its low cost, convenience of transfer, and ease of blending and production. MTBE has become a prevalent groundwater contaminant because it is widely used and it has been disposed inappropriately. MTBE has been demonstrated an animal carcinogen. The US Environmental Protection Agency (US EPA) has temporarily classified MTBE as a possible human carcinogen and has set its advisory level for drinking water at 20-40 µg/L based on taste and odor concerns. The Taiwan Environmental Protection Administration (TEPA) also classifies it as the Class IV toxic chemical substances. Currently, natural attenuation (NA) as well as natural bioremediation or enhanced bioremediation are attractive remediation options for contaminated sites due to their economic benefit and environmental friendly. In general, in situ microorganisms at the contaminated site play a very important role in site restoration. Although early studies suggested that the biodegradability of MTBE was not significant, recent laboratory and field reports reveal that MTBE can be biodegraded under aerobic and anaerobic conditions. In addition, evidences and some successful cases of MTBE attenuation have been reported that make natural attenuation a considerable remedial strategy. However, the biodegrading rate might decrease if the nutritional and physiological requirements are not met. Thus, it is important to assess the biodegradability of natural microorganisms under various site conditions to obtain optimal remedial conditions. Contributions of intrinsic biodegradation and other abiotic mechanisms to the removal and control of contaminants should also be evaluated to provide sufficient information for remedial option determination. Moreover, isolation and identification of the dominant native microorganisms will be helpful to following remediation tasks. In the first part of this study, microcosm study and microbial identification technologies (denaturing gradient gel electrophoresis, DGGE) were applied to assess the biodegradability of MTBE by indigenous microbial consortia and to identify the dominant microorganisms at a MTBE-contaminated site (Site A). In the second part of this study, thorough field investigations were performed to evaluate the occurrence of natural attenuation of MTBE at two MTBE-contaminated sites (Site A and Site B). In addition, a natural attenuation model, BIOSCREEN, was performed to assess the effectiveness of natural attenuation on MTBE containment. The main objectives of this study contained the following: (1)Evaluate MTBE biodegradability under different redox conditions by the indigenous microorganisms. (2)Determine the dominant native microorganisms in MTBE biodegradation for further application. (3)Assess the feasibility of using natural attenuation to control the MTBE plume. (4)Evaluate the contributions of intrinsic biodegradation patterns on natural attenuation processes by BIOSCREEN. Results from the microcosm study reveal that MTBE could be biodegraded by aquifer sediments without the addition of extra carbon sources under aerobic conditions. The production of tert-butyl alcohol (TBA), a degradation byproduct of MTBE, was detected. Complete removal of TBA was also observed by the end of the experiment. Results from aerobic microcosms study indicate that oxygen might be the major limiting factor of MTBE biodegradation at Site A. Thus, MTBE at this site could be removed via natural biodegradation processes with the supplement of sufficient oxygen. Microcosm study with extracted supernatant of aquifer sediments as the inocula show that the indigenous microorganisms were capable of using MTBE as the sole carbon and energy source. The calculated MTBE degradation rate was 0.597 mg/g cells/h or 0.194 nmole/mg cells/h. No MTBE removal was observed under various anaerobic conditions. Results suggest that aerobic biodegradation was the dominant degradation process and aerobic bioremediation might be a more appropriate option for the site remediation. According to the results of DGGE analysis, aerobic MTBE-biodegrading bacteria, Pseudomonas sp. and Xanthomonas sp., might exist at this site. Although results of microcosm study show that MTBE could not be degraded under anaerobic conditions, the microbial identification indicates that some novel anaerobic microbes, which could degraded MTBE, might be present at this site. In addition, anaerobic microbes caused the consumption of electron acceptors (e.g., nitrate, ferric iron) and removal of benzene, toluene, ethylbenzene, xylenes (BTEX), 1,2,4-trimethyl benzene (1,2,4-TMB), and 1,3,5-trimethyl benzene (1,3,5-TMB) (TMBs) in the anaerobic microcosms. These results also indicate that the potential of anaerobes activities was high at Site A. Based on the results from the field investigation, natural attenuation of MTBE was occurring at both sites. MTBE plume at Site B could be effectively controlled via natural attenuation processes. Nevertheless, MTBE plume at Site A has migrated to a farther downgradient area and passed the boundary of the site. Field investigation results indicate that the natural attenuation mechanisms of MTBE at both sites were occurring with the first-order attenuation rates of 0.0021 and 0.0048 1/day at Sites A and B, respectively. According to BIOSCREEN simulation, biodegradation was responsible for 78% and 59% of MTBE mass reduction at Sites A and B, respectively. The intrinsic biodegradation had significant contributions on the control of MTBE plumes. Moreover, the dilution and dispersion processes might be the major mechanisms for the attenuation of MTBE in the downgradient areas. However, results also reveal that intrinsic biological processes might still fail to contain the plume if the selected point of compliance is not appropriate. Results of this study suggest that natural attenuation might be feasible to be used as a remedial option for the remediation of MTBE-contaminated site on the premise that (1) detailed site characterization has been conducted, and (2) the occurrence and effectiveness of natural attenuation processes have been confirmed. Based on the results from the field investigation and laboratory microcosm studies, MTBE could be biodegraded by natural microbial populations at the studied sites under both aerobic and anaerobic conditions and natural attenuation would be applied as a remedial option at MTBE-contaminated sites. Results from this study would be useful in determining the favorable bioremediation conditions and designing an efficient and cost-effective bioremediation system such as monitored natural attenuation (MNA) or in situ or on-site MTBE bioremediation system for field application.