A two-stage, sequential inoculation bioreactor strategy for the bioremediation of groundwater contaminated with creosote and pentachlorophenol (PCP) was evaluated at bench scale (1.2 L) and pilot scale (454 L). Bioreactor performance using specially selected microorganisms was assessed according to chemical analyses of system influent, effluent, and bioreactor residues, a chemical mass balance evaluation, and comparative biological toxicity and teratogenicity measurements. During pilot-scale operations, the concentration of creosote constituents was reduced from ca. 1000 ppm in the groundwater feed (flow rate 114 L/day) to <9 ppm in the system effluent (total removal efficiency of >99%). Notably, the cumulative concentration of carcinogenic polycyclic aromatic hydrocarbons was reduced from 368 ppm in the feed to 5.2 ppm in the system effluent. Moreover, the toxicity and teratogenicity of the bioreactor effluent were significantly reduced. In general, field data correlated well with those obtained from bench-scale studies.f Research contribution no. 822 of the Gulf Breeze Environmental Research Laboratory.

The effect of the presence of more easily degradable alternative carbon sources on the biodegradation of toxic waste components is of great practical importance. In this work, a mixed phenol/glucose waste was fed to two heterogeneous populations acclimated to different conditions: one was acclimated to phenol as a sole source of carbon and one to a mixed phenol/glucose substrate. Batch substrate utilization experiments were performed under both growth and nonproliferating (no medium nitrogen source) conditions in order to assess substrate removal patterns at the levels of enzyme production and enzyme function. The results indicated that the substrate removal pattern exhibited by the cells was significantly influenced by the acclimation characteristics of the culture. The phenol acclimated cells showed an initial preference for phenol, but the presence of glucose hindered phenol removal rate under both growth and nonproliferating conditions. The cells acclimated to the mixed phenol/glucose waste demonstrated rapid initial glucose removal with a slower concomitant utilization of phenol; acclimation to the mixed waste evidently had a significant impact on the substrate removal pattern for this mixed substrate system.

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