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Applied and Environmental Microbiology, February 2008, p. 667-675, Vol. 74, No. 3
0099-2240/08/$08.00+0     doi:10.1128/AEM.00717-07
Copyright © 2008, American Society for Microbiology. All Rights Reserved.

Effect of pH on Intracellular Accumulation of Trace Concentrations of Hg(II) in Escherichia coli under Anaerobic Conditions, as Measured Using a mer-lux Bioreporter{triangledown}

George R. Golding,1,{dagger} Richard Sparling,1* and Carol A. Kelly2,{ddagger}

Department of Microbiology, University of Manitoba, Winnipeg, Manitoba R3T 2N2, Canada,1 Freshwater Institute, Department of Fisheries and Oceans, 501 University Crescent, Winnipeg, Manitoba R3T 2N6, Canada2

Received 29 March 2007/ Accepted 30 November 2007

The effects of pH on the uptake and accumulation of Hg(II) by Escherichia coli were determined at trace, environmentally relevant, concentrations of Hg and under anaerobic conditions. Hg(II) accumulation was measured using inducible light production from E. coli HMS174 harboring a mer-lux bioreporter plasmid (pRB28). The effect of pH on the toxicity of higher concentrations of Hg(II) was measured using a constitutive lux plasmid (pRB27) in the same bacterial host. In this study, intracellular accumulation and toxicity of Hg(II) under anaerobic conditions were both significantly enhanced with decreasing pH over the pH range of 8 to 5. The pH effect on Hg(II) accumulation was most pronounced at pHs of <6, which substantially enhanced the Hg(II)-dependent light response. This enhanced response did not appear to be due to pH stress, as similar results were obtained whether cells were grown at the same pH as the assay or at a different pH. The enhanced accumulation of Hg(II) was also not related to differences in the chemical speciation of Hg(II) in the external medium resulting from the changes in pH. Experiments with Cd(II), also detectable by the mer-lux bioreporter system, showed that Cd(II) accumulation responded differently to pH changes than the net accumulation of Hg(II). Potential implications of these findings for our understanding of bacterial accumulation of Hg(II) under anaerobic conditions and for bacteria-mediated cycling of Hg(II) in aquatic ecosystems are discussed. Arguments are provided suggesting that this differential accumulation is due to changes in uptake of mercury.

* Corresponding author. Mailing address: University of Manitoba, Department of Microbiology, Winnipeg, MB, Canada R3T 2N2. Phone: (204) 474-8320. Fax: (204) 474-7603. E-mail: Richard_sparling{at}umanitoba.ca

{triangledown} Published ahead of print on 14 December 2007.

{dagger} Present address: National Microbiology Laboratory, 1015 Arlington Ave., Winnipeg, MB, Canada R3E 3R2.

{ddagger} Present address: R&K Research Inc., 675 Mt. Belcher Heights, Salt Spring Island, BC, Canada V8K 2J3.

Applied and Environmental Microbiology, February 2008, p. 667-675, Vol. 74, No. 3
0099-2240/08/$08.00+0     doi:10.1128/AEM.00717-07
Copyright © 2008, American Society for Microbiology. All Rights Reserved.





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