Aerobic,phenol-induced TCE degradation in completely mixed,continuous-culture reactors

BothPseudomonas putida F1 and a mixed culture were used to study TCE degradation in continuous culture under aerobic, non-methanotrophic conditions. TCE mass balance studies were performed with continuous culture reactors to determine the total percent removed in the reactors, and to quantify the percent removed by air stripping and biodegradation. Adsorption of TCE to biomass was assumed to be negligible. This research demonstrated the feasibility of treating TCE-contaminated water under aerobic, non-methanotrophic conditions with a mixed-culture, continuous-flow system.Initially glucose and acetate were fed as primary substrates. Pnenol, which has been shown to induce TCE-degrading enzymes, was fed at a much lower concentration (20mg/L). Little degradation of TCE was observed when acetate and glucose were the primary substrates. After omitting glucose and acetate from the feed and increasing the phenol concentration to 50mg/L, TCE biotransformation was observed at a significant level (46%). When the phenol concentration in the feed was increased to 420mg/L, 85% of the incoming TCE was estimated to have been biodegraded. Under the same conditions, phenol utilization by the mixed culture was greater than that ofP. putida F1, and TCE degradation by the mixed culture (85%) exceeded that ofP. putida F1 (55%). The estimated percent-of-TCE biodegraded by the mixed culture was consistently greater than 80% when phenol was fed at 420mg/L. Biodegradation of TCE was also observed in mixed-culture, batch experiments.     

Influence of systems biology response and environmental exposure level on between-subject variability in breath and blood biomarkers

To explain the underlying causes of apparently stochastic disease, current research is focusing on systems biology approaches wherein individual genetic makeup and specific ‘gene–environment’ interactions are considered. This is an extraordinarily complex task because both the environmental exposure profiles and the specific genetic susceptibilities presumably have large variance components. In this article, the focus is on the initial steps along the path to disease outcome namely environmental uptake, biologically available dose, and preclinical effect. The general approach is to articulate a conceptual model and identify biomarker measurements that could populate the model with hard data. Between-subject variance components from different exposure studies are used to estimate the source and magnitude of the variability of biomarker measurements. The intent is to determine the relative effects of different biological media (breath or blood), environmental compounds and their metabolites, different concentration levels, and levels of environmental exposure control. Examples are drawn from three distinct exposure biomarker studies performed by the US Environmental Protection Agency that studied aliphatic and aromatic hydrocarbons, trichloroethylene and methyl tertiary butyl ether. All results are based on empirical biomarker measurements of breath and blood from human subjects; biological specimens were collected under appropriate Institutional Review Board protocols with informed consent of the subjects. The ultimate goal of this work is to develop a framework for eventually assessing the total susceptibility ranges along the toxicological pathway from exposure to effect. The investigation showed that exposures are a greater contributor to biomarker variance than are internal biological parameters.     

Exposure and Health Risk from Swimming in Outdoor Pools Contaminated by Trichloroethylene

A method was developed that evaluated the exposure and health risk to children from swimming in outdoor pools filled with contaminated water. It was found that dermal absorption of trichloroethylene (TCE) was significantly larger than the inhalation component of the exposures. It was estimated that the inhalation route accounted for only 1% of the total exposure, whereas accidental ingestion was 7% of the child's total intake and the dermal absorbed dose was 92% of the total exposure. The relative percentage of the total exposure estimated for each exposure route indicated that the dermal exposure route and accidental ingestion of pool water should not be ignored for volatile compounds when evaluating exposure.

The method utilized was simple enough to use computer spreadsheets for the calculations and can be easily adapted to various swimming scenarios and age groups. This method also included an assessment of the uncertainty in the exposure and risk estimates. The range of estimated exposures was 40 μ g to 442 μ g of TCE per swimming season. All values in this range were below the health benchmark for both non-carcinogenic and carcinogenic endpoints.     

Development and operation of a trickling biofilter system for continuous treatment of gas-phase trichloroethylene

A parallel trickling biofilter (TBF) system that consists of two TBFs units in parallel, one for biodegradation of trichloroethylene (TCE) and the other for reactivation of an inactivated biofilm, was developed and operated for continuous treatment of gas-phase TCE by Burkholderia cepacia G4. For inlet loadings below 8.6 mg TCE l^–1 d^–1, complete removal of TCE was achieved. The maximal TCE elimination capacity was 17 mg l^–1 d^–1.     

Biodegradation of Trichloroethylene and Dichloromethane in Contaminated Soil and Groundwater

Soil column and serum bottle microcosm experiments were conducted to investigate the potential for in situ anaerobic bioremediation of trichloroethy lene (TCE) and dichloromethane (DCM) at the Pinellas site near Largo, Florida. Soil columns with continuous groundwater recycle were used to evaluate treatment with complex nutrients (casamino acids, methanol, lactate, sulfate); benzoate and sulfate; and methanol. The complex nutrients drove microbial dechlorination of TCE to ethene, whereas the benzoate/sulfate and methanol supported microbial dechlorination of TCE only to cis-1 ,2-dichloroethylene (cDCE). Microbial sulfate depletion in the benzoate/sulfate column allowed further dechlorination of cDCE to vinyl chloride. Serum bottle microcosms were used to investigate TCE dechlorination and DCM biodegradation in Pinellas soil slurries bioaugmented with liquid from the soil columns possessing TCE-dechlorinating activity and DCM biodegradation by indigenous microorganisms. Bioaugmented soil microcosms showed immediate TCE dechlorination in the microcosms with methanol or complex nutrients, but no dechlorination in the benzoate/sulfate microcosm. DCM biodegradation by indigenous microorganisms occurred in soil microcosms amended with either benzoate/sulfate or methanol, but not with complex nutrients. Bioaugmentation stimulated DCM biodegradation in both complex nutrient and methanol-amended microcosms, but appeared to inhibit DCM biodegradation in benzoate/sulfate-amended microcosms. TCE dechlorination occurred before DCM biodegradation in bioaugmented microcosms when both compounds were present.     

Kinetic analysis of the inhibitory effect of trichloroethylene (TCE) on nitrification in cometabolic degradation

In this study, the inhibitory effect of TCE on nitrification process was investigated with an enriched nitrifier culture. TCE was found to be a competitive inhibitor of ammonia oxidation and the inhibition constant (K _I ) was determined as 666–802 μg/l. The TCE affinity for the AMO enzyme was significantly higher than ammonium. The effect of TCE on ammonium utilization was evaluated with linearized plots of Monod equation (e.g., Lineweaver–Burk, Hanes–Woolf and Eadie–Hofstee plots) and non-linear least square regression (NLSR). No significant differences were found among these data evaluation methods in terms of kinetic parameters obtained.     

Historical drinking water contamination at Camp Lejeune: Regulatory risk assessor and personal perspectives

Historical concentrations of trichloroethylene (TCE) and other chemicals in drinking water at the U.S. Marine Corps Base at Camp Lejeune, NC, were sufficiently elevated to raise potential health concerns. The 1952–1984 mean TCE concentration (138 µg/L) exceeded the U.S. Environmental Protection Agency's (USEPA's) current maximum contaminant level (MCL) of TCE by 28-fold, with the corresponding dose (3.9E–03 mg/kg-day) exceeding all three candidate USEPA reference dose (RfD) values by 8- to 11-fold. Today, TCE hazard quotients (HQs) of 8–11 compel immediate action by USEPA. The mean dose also exceeds the supporting RfD values for toxic nephropathy and increased kidney weight, as well as the point of departure (POD) for toxic nephropathy. Furthermore, the estimated doses for 34% of the 9-month rolling averages exceed the POD for the highest RfD value for fetal heart defects. The incidences of nephropathy and fetal heart defects should be thoroughly evaluated among those who were exposed. Long-term follow-up will be required to assess potential health effects for the 500,000 to 1 million people who may have used the contaminated water at Camp Lejeune or were exposed in utero. This should serve as a cautionary tale for the thousands of Department of Defense sites across the USA (and other similarly contaminated sites elsewhere in the world) that are commonly contaminated with chemicals such as those at Camp Lejeune, where necessary sampling should be conducted to identify and mitigate any likely ongoing (or future) exposures of potential health concern.     

Evaluation of trichloroethylene degradation by E. coli transformed with dimethyl sulfide monooxygenase genes and/or cumene dioxygenase genes

Pseudomonas fluorescens IP01 grown on isopropylbenzene (cumene) and Acinetobacter sp. 20B grown on dimethyl sulfide (DMS) degraded up to 90% and 25% of 1.5 mg trichloroethylene (TCE)/l, respectively. Escherichia coli harboring the DMS monooxygenase genes from strain 20B, the cumene dioxygenase genes from strain IP01 and both oxygenase genes, degraded up to 50%, 75% and 88% of 75 mg TCE/l, respectively. The growth rates of the E. coli recombinants remained nearly unaffected by TCE at 15 150 mg/l. Thus, the E. coli recombinants were indicated to degrade high concentrations of TCE efficiently at least up to 150 mg l–1.     

中国典型特大城市交通的生态足迹评价

中国城市化快速发展带来机动车数量的骤增、交通拥堵、交通污染物排放及能源消耗恶化等城市生态问题,生态足迹可以作为衡量城市交通发展带来生态环境压力的有效指标。本文以北京、上海、天津、杭州、沈阳和成都6个特大城市为研究对象,计算了2005—2012年6个城市的交通生态足迹。结果表明:6个城市交通的生态足迹均有所增加,城市交通的生态环境压力逐年增加,化石能源间接生态足迹在城市交通生态足迹增长中起到主要作用;快速增长的机动车和小汽车及其高出行率导致能源消耗不断增加,是城市交通生态足迹增长的主要原因;完善的轨道交通及慢行交通等绿色出行的发展,可以有效降低特大城市自驾出行的次数,优化交通出行结构,缓解城市交通生态环境压力。