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Biodegradation of chlorinated aliphatic hydrocarbon mixtures in a single-pass packed-bed reactor
Author(s) -
Laura W. Lackey,
Tommy J. Phelps,
Paul R. Bienkowski,
David White
Publication year - 1993
Publication title -
applied biochemistry and biotechnology
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.558
H-Index - 111
eISSN - 1559-0291
pISSN - 0273-2289
DOI - 10.1007/bf02919029
Subject(s) - tetrachloroethylene , biodegradation , trichloroethylene , packed bed , bioreactor , chemistry , effluent , methane , hydrocarbon , environmental chemistry , chemical oxygen demand , chromatography , environmental engineering , environmental science , organic chemistry , sewage treatment
Aliphatic chlorinated compounds, such as trichloroethylene (TCE) and tetrachloroethylene (PCE), are major contaminants of ground water. A single-pass packed-bed bioreactor was utilized to study the biodegradation of organic waste mixtures consisting of PCE, TCE, and other short-chain chlorinated organics. The bioreactor consisted of two 1960-mL glass columns joined in a series. One column was packed with sand containing a microbial consortia enriched from a contaminated site. The other column provided a reservoir for oxygen and a carbon source of methane/propane that was recirculated through the reactor. Sampling was accomplished by both direct headspace and liquid effluent concentration analyses. The reactor was operated in a single-pass mode. Greater than 99% degradation of trichloroethylene, approaching drinking water standards, was observed when the bioreactor residence time ranged from 1.9 to 3.2 d. Typically, when the reactor was pulse-fed with methane, propane, and air, 1 mol of TCE was degraded/110 mol of substrate utilized. Perturbation studies were performed to characterize reactor behavior. The system's degradation behavior was affected by providing different carbon sources, a pulse feeding regime, supplementing microbial biomass, and by altering flow rates.

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