Abstract

Trichloroethylene (TCE) is a common groundwater contaminant of toxic and carcinogenic concern. Aerobic co-metabolic processes are the predominant pathways for TCE complete degradation. In this study, Pseudomonas fluorescens was studied as the active microorganism to degrade TCE under aerobic condition by co-metabolic degradation using phenol and gasoline as growth substrates. Operating conditions influencing TCE degradation efficiency were optimized. TCE co-metabolic degradation rate reached the maximum of 80% under the optimized conditions of degradation time of 3 days, initial OD600 of microorganism culture of 0.14 (1.26 × 107 cell/mL), initial phenol concentration of 100 mg/L, initial TCE concentration of 0.1 mg/L, pH of 6.0, and salinity of 0.1%. The modified transformation capacity and transformation yield were 20 μg (TCE)/mg (biomass) and 5.1 μg (TCE)/mg (phenol), respectively. Addition of nutrient broth promoted TCE degradation with phenol as growth substrate. It was revealed that catechol 1,2-dioxygenase played an important role in TCE co-metabolism. The dechlorination of TCE was complete, and less chlorinated products were not detected at the end of the experiment. TCE could also be co-metabolized in the presence of gasoline; however, the degradation rate was not high (28%). When phenol was introduced into the system of TCE and gasoline, TCE and gasoline could be removed at substantial rates (up to 59% and 69%, respectively). This study provides a promising approach for the removal of combined pollution of TCE and gasoline.

Highlights

  • Trichloroethylene (TCE) has been widely used as a solvent for the past 70 years

  • This study investigated the aerobic co-metabolic degradation of TCE in aqueous phase by Pseudomonas fluorescens using phenol as the main growth substrate

  • The primary cause of the nutrient broth promotion effect was the increase of cells, which generated an active enzyme system stimulated by phenol

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Summary

Introduction

Trichloroethylene (TCE) has been widely used as a solvent for the past 70 years. Because of improper disposal practices for spent solvents in the past, TCE has become a major contaminant in groundwater [1]. An estimated 852 out of 1430 National Priorities List sites identified by the US EPA are contaminated with TCE [2]. In China, the annual production of TCE was 2.5 × 105 ton in. TCE is listed as one of the 68 priority pollutants in aquatic environment. TCE pollution in groundwater has been reported in several cities, such as Kaifeng, Henan province; Xuzhou, Jiangsu province; and Shanghai [4,5,6]. TCE concentration up to 63.7 μg/L has been reported in Beijing [7]

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