Water Air & Soil Pollution

, Volume 56, Issue 1, pp 465-475

First online:

Environmental applications of mercury resistant bacteria

  • Franco BaldiAffiliated withDepartment of Environmental Biology, University of Siena
  • , Franca SempliciAffiliated withDepartment of Environmental Biology, University of Siena
  • , Marco FilippelliAffiliated withChemistry Laboratory of Hygiene and Prophylaxis

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Bacteria are resistant to Hg compounds by virtue of two specific enzymes: mercuric reductase and organomercurial lyase. We investigate these specific enzyme systems 1) to determine McHg in biological samples by its enzymatic transformation to the respective hydrocarbon and 2) as an environmental index of Hg pollution in geothermal areas, by studying the distribution of the percentage of Hg-resistant bacteria.

The first application is based on the enzymatic conversion of McHg to CH4. by whole cells of the Pseudomonas putida strain FBI. A 1 ml aliquot of 0.01N aqueous solution of thiosulphate containing MeHg, extracted from a biological sample by a conventional procedure was mixed with a dense (1 mg cells/mL dw) culture of FBI strain in a microreaction vessel. After a suitable period of incubation (from 4 to 18 hours), methane was assayed in the headspace by gas chromatograph equipped with flame ionization detector.

In the second application, Hg-resistant bacteria (MRB) isolated from mosses collected in a geothermal area (Travale) in Tuscany showed almost the same distribution pattern as total Hg in briophytes. Mosses and MRB are both suitable bioindicators for mapping contaminated areas. The finding of Hg-resistant strains depends on the availability of the metal for cell accumulation and interaction at molecular level in the cytoplasm to produce mercuric reductase. MRB/g dw is therefore an indirect measure of the enzyme in this terrestrial geothermal environment.