Lithotrophic Bacterial Leaching of Heavy Metals from Sediments Dredged from the Deûle Canal, France
N. Y. Sabra1, H. C. Dubourguier2, A. Benmimouna2, M. N. Duval2, S. Camuzeaux2, T. Hamieh*, 1, 3
Identifiers and Pagination:Year: 2011
First Page: 18
Last Page: 29
Publisher Id: TOENVIRJ-5-18
Article History:Received Date: 16/12/2009
Revision Received Date: 23/11/2010
Acceptance Date: 09/12/2010
Electronic publication date: 18/11/2011
Collection year: 2011
open-access license: This is an open access article distributed under the terms of the Creative Commons Attribution 4.0 International Public License (CC-BY 4.0), a copy of which is available at: https://creativecommons.org/licenses/by/4.0/legalcode. This license permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Lithotrophic bacterial leaching of heavy metals from dredged sediments was studied in semi-pilot scale air-lift bioreactors. Prior to the bioleaching experiments, a physico-chemical characterization of the sediments comprising a sequential extraction study was conducted. The sediments turned out to be highly loaded with heavy metals, and with the exception of managanese, mainly associated to the oxidizable fraction of the sediments and thus strongly linked to the latter. The heavy metals could be classified by decreasing order of mobility as follows: Mn>Zn>Cu>Cd>Pb.
The bacterial leaching was found to be strongly dependent on the nature of the mineral substrate. Sulfur gave the best solubilization results in comparison with reduced iron or with a combination of reduced iron and sulfur. In the presence of oxygen, lithotrophic bacteria oxidized sulfur into sulfates and induced an acidification of the sediments. These conditions led to the release of the metals that were tightly linked to the sediments, that is those associated with the sulfides and/or with the organic matter. With sulfur as a substrate, the solubilization percentages varied within 30 days between 72 and 93% of the total sediment content (wt/wt) for cadmium, copper, manganese and zinc. Much lower biosolubilization percentages were obtained in the case of lead because of the poor solubility of lead sulfate.