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Bacterial adherence to abiotic support plays a major role in bioremediation, biocatalysis or microbial fuel cells. Bioremediation processes use the capacities of microorganisms to degrade organic substances, or to modify the metal distribution (immobilization, volatilization) or speciation. These beneficial activities are observed in aquatic and terrestrial ecosystems, but also in the artificial systems developed to treat polluted water of industrial and domestic wastes. The intensity and the quality of the microbial activity depend on physico-chemical factors, but also on the lifestyle of microorganisms (free-floating or embedded into biofilm). The biofilm formation is associated with a metabolism promoting resistance to biocides by diverse mechanisms. This phenomenon will therefore be encouraged in most bioremediation processes. Moreover, engineering Escherichia coli cells to control the biofilm formation has been successfully applied to immobilize whole-cell sensors on biochips2-3.
Adaptation of microorganisms to high concentration of metals occurs via diverse mechanisms such as adsorption to extracellular matrix components, activation of efflux pump or specific carriers able to concentrate the metal into the cell. Boosting these bacterial activities via genetic engineering allows efficient and cheap treatment of metal pollution at the laboratory scale, especially in the case of highly toxic metals in weak quantity as described by Raghu et al. 2008 4. Bacterial remediation represents in this case a competitive and cost saving method compared to classical chemical processes using ion exchange resins. The authors described an E. coli chassis genetically engineered for cobalt uptake and retention first by knocking out the efflux pump encoding gene rcnA, and then by transformation with a multi copy plasmid allowing overproduction of a transporter with preferential uptake for cobalt. Such a strain appears as an efficient alternative to ion exchange resins to treat radioactive effluent, but a key unresolved issue is the recovery of contaminated bacteria at the end of the process 4. The objective of our work was therefore to engineer a custom-designed strain able to stick to abiotic supports such as glass or plastic.
Amongst the whole set of adhesins and adherent fimbriae identified in Gram- bacteria, we chose to design a system allowing curli production. Curli are thin (2-5 nm diameter) and highly aggregative amyloid fibers that protrude from the E. coli and Salmonella surface as a non-crystalline and insoluble matrix 5-7. Curli are also involved in the colonization of abiotic surfaces and the development of biofilms 8. Curli were recently shown to bind mercury ions 9. Amyloids are indeed known to possess high affinity for metals ions such as Cu2+, Zn2+ and Fe3+ 10. This property might further improve the decontamination of metal polluted effluents. The csg cluster is responsible for the production of curli fibers and is constituted of two divergently transcribed operons (Figure 1). The csgB, csgA and csgC genes constitute the sense operon, encoding the two curli subunits, CsgA and CsgB. CsgC seems to be involved in redox activity within the curli biogenesis system and to affect CsgG pore behavior 11. However, the absence of csgC in the majority of curli-producing bacteria indicates that the corresponding protein provides only a secundary level of control over the curli biogenesis. To simplify the system, we have been chosen to work with the minimum number of genes.
The csgDEFG operonencodes proteins essential in the regulation and transportation of CsgA and CsgB to the cell surface. CsgD is a transcriptional activator of the csgBAC operon and plays a key role in the control of biofilm formation by controlling the production of curli fimbriae and other biofilm components such as cellulose 12 and by inhibiting the flagellum production 13. CsgE, CsgF and CsgG constitute a curli-specific secretory apparatus in the outer-membrane through which the major curli subunit protein CsgA is secreted as a soluble protein. The polymerization of CsgA is dependent in vivo on the membrane-bound nucleator protein CsgB (reviewed in 14). Complex regulatory pathways involving several two-component systems have been shown to control curli gene expression 15-16. These complex regulations allow bacteria to form thick biofilms via the curli production in response to environmental cues, but are difficult to control for industrial applications. To facilitate the recovery of the metal-stuffed bacteria during an industrial process, bacterial fixation to a solid support indeed needs to be controlled by well defined parameter(s). The adherent properties of curli are linked to their amyloid nature 17 and could be used to improve bioremediation processes, but a simpler and easily controlled device has to be created.
Amongst these 7 genes 18, a set of 5 absolutely required genes for curli synthesis (csgB and csgA encoding fiber monomers) and export (csgE csgF and csgG, encoding the curli secretion complex) were selected to construct the synthetic operon. To escape the "natural" regulation of curli, a synthetic operon comprising these 5 csg genes under the control of a strong and cobalt-overinducible promoter (Figure 2) was designed and synthesized. The step-by-step analysis of the curli-encoding region and the design procedure for a functional synthetic operon are described. Two methods to visualize and quantify bacterial adherence to polystyrene and glass are explained.