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Despite growing interest in the electro-bioremediation of contaminated soil it is still largely unknown to which degree weak electric fields influence the fate of contaminant-degrading microorganisms in the sub-surface. Here we evaluate the factors influencing the electrokinetic transport and deposition of fluorene-degrading Sphingomonas sp. LB126 in a laboratory model aquifer exposed to a direct current (DC) electric field (1 V cm(-1)) typically used in electro-bioremediation measures. The influence of cell size, cell membrane integrity, cell chromosome contents (all assessed by flow cytometry), cell surface charge and cell hydrophobicity on the spatial distribution of the suspended and matrix-bound cells after 15 h of DC-treatment was evaluated. In presence of DC the cells were predominantly mobilised by electroosmosis to the cathode with an apparent velocity of 0.6 cm h(-1), whereas a minor fraction only of the cells augmented was mobilised to the anode by electrophoresis. Different electrokinetic behaviour of individual cells could be solely attributed to intra-population heterogeneity of the cell surface charge. In the absence of DC by contrast, a Gaussian-type distribution of bacteria around the point of injection was found. DC had no influence on the deposition efficiency, as the glass beads in presence and absence of an electric field retained quasi-equal fractions of the cells. Propidium iodide staining and flow cytometry analysis of the cells indicated the absence of negative influences of DC on the cell wall integrity of electrokinetically mobilised cells and thus point at unchanged physiological fitness of electrokinetically mobilised bacteria.

An extension of the models developed by Guha and Jaffé (Biotechnol Bioeng [1996] 50:693-699) to describe the phenanthrene biodegradation kinetics for the cultures with variable fractional volumes is presented. Batch experiments were conducted with a culture capable of degrading the phenanthrene using a single culture vessel from which samples were withdrawn over time to monitor the disappearance of phenanthrene. For accurate measurement of phenanthrene concentrations, a sampling procedure designed for quantifying the sorption of phenanthrene onto glassware was also introduced. The Monod parameters were estimated by nonlinear regression analyses of simultaneous solutions to the substrate utilization/volatilization and Monod equations for growth of the cell mass. The results demonstrate that the models were able to be extended to phenanthrene-degrading cultures with variable fractional volumes. When the ratio between sampling volume and volume of the culture medium was relatively small, the parameters obtained were similar to those which would be obtained using constant fractional volumes of culture medium. It was also found that the model's fit to the phenanthrene disappearance data in this study were better than those obtained by Guha and Jaffé, implying that the sorption process of phenanthrene during the sampling period could significantly affect the measurement of phenanthrene concentrations. Failing to account for these losses led to less accurate measurements of substrate concentrations, which in turn resulted in a poor estimation of the parameters. The findings of this study reduce considerably the experimental work necessary in the estimation of Monod kinetic parameters for the purpose of modeling., (Copyright 2004 Wiley Periodicals, Inc.)