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1 Unité de Biologie des Spirochètes, Institut Pasteur, 75724 Paris Cedex 15, France
2 Instituto de Microbiologia Professor Paulo de Góes, Universidade Federal do Rio de Janeiro, Brazil
3 Plate-Forme de Microscopie Électronique, Institut Pasteur, Paris, France
4 Instituto Biomédico, Universidade Federal Fluminense, Brazil
Correspondence
Mathieu Picardeau
mpicard{at}pasteur.fr
| ABSTRACT |
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The GenBank/EMBL/DDBJ accession numbers for the complete genomic sequence of L. biflexa serovar Patoc strain Patoc1 are CP000786, CP000787 and CP000788.
| INTRODUCTION |
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Leptospira spp. belong to the bacterial phylum of Spirochaetes, an evolutionarily and structurally unique group of bacteria. These bacteria are composed of both saprophytic and pathogenic members, such as Leptospira biflexa and Leptospira interrogans, respectively (Faine et al., 1999
). Leptospires are motile, obligately aerobic, and slow-growing bacteria that have an optimal growth temperature of 30 °C. They are able to survive in soil and water for long periods (Henry & Johnson, 1978
; Trueba et al., 2004
). Pathogenic species are the causal agents of leptospirosis, a widespread zoonosis that is a major public health problem in developing countries in South-East Asia and South America. In the animal reservoirs of the disease such as rodents, infection produces chronic and persistent asymptomatic carriage in the renal tubules and bacteria are then excreted in urine. Humans are usually infected through cut or abraded skin contact with water contaminated by the urine of animal reservoirs (McBride et al., 2005
). More than 500 000 cases of severe leptospirosis occur each year, with a mortality rate of 5–20 % (WHO, 1999
).
Because of the association of both saprophytic and pathogenic leptospires with water sources, we sought to characterize biofilm development by these micro-organisms. Although Singh et al. (2003)
revealed the presence of Leptospira spp. in biofilms of dental water unit systems by 16S rDNA sequencing, biofilm formation by these organisms has not been characterized to our knowledge. Among the order Spirochaetales, only Treponema denticola, which is phylogenetically distant from leptospires, was shown to form biofilms in vitro (Vesey & Kuramitsu, 2004
).
Biofilm formation by Leptospira spp. may play an important role in their ability to survive in diverse environmental habitats, including in the host. This paper describes, for the first time to our knowledge, the characteristics of Leptospira spp. biofilms. We also discuss the possible roles of these biofilms in the lifestyles of these bacteria.
| METHODS |
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Biofilm formation was tested in glass tubes with 10 ml EMJH liquid medium. Tubes were incubated at 30 °C for a period of 2 months and cultures were observed daily for the formation of surface-associated biofilms at the air–liquid interface and floating biofilms, i.e. floating pellicles that cover the liquid medium surface (Table 1
). Biofilm production of L. biflexa was also assessed in a low-nutrient environment (inoculation of a 1 ml exponential-phase culture grown in EMJH into 9 ml mineral water). For this purpose, L. biflexa was cultured in glass tubes with filter-sterilized natural mineral water. Biofilm production in commercially available non-carbonated natural mineral water [pH 6.8; mineral content (mg l–1): Na+, 2.7; K+, 0.9; Ca2+, 7.1; Mg2+, 2; Cl–, 2;
, 6.6;
, 2;
, 24] was investigated over 2 weeks.
Biofilm formation was measured in 12-well polystyrene plates (flat-bottom wells, tissue culture treated; Corning) with 700 µl EMJH liquid medium. Polystyrene plates were sealed during incubation to avoid desiccation. At different time points, the liquid culture was removed by aspiration and the wells were gently rinsed once with distilled water to remove non-adherent planktonic cells. Surface-associated cells were air-dried for 15 min and fixed with 2 % sodium acetate. The sodium acetate solution was removed by aspiration and surface-associated cells were allowed to dry again. Cells were then stained with 900 µl 1 % crystal violet solution for 20 min. The crystal violet was removed by aspiration, and the wells were carefully rinsed three times in distilled water. Crystal violet remaining in the wells was then dissolved in 1 ml of an ethanol/acetone (v/v 80/20) solution and the A600 was measured.
Light microscopy of biofilms.
Glass slides (76x26 mm, Menzel-Glaser) were incubated half submerged in a bacterial suspension (initial concentration 106 bacteria ml–1) and observed at different times (1, 6, 16, 24, 40, 48, 64, 72, 160 and 190 h). After incubation, slides were rinsed three times in distilled water, air-dried, fixed by heating and observed by phase-contrast microscopy using a Nikon FXA microscope (200x magnification).
Electron microscopy of biofilms.
For electron microscopy, glass coverslips (18x18 mm, Menzel-Glaser) were placed into wells of 12-well polystyrene plates (Corning) with 2 ml of a bacterial suspension at 106 bacteria ml–1 for L. biflexa and at 5x106 bacteria ml–1 for L. interrogans, and cultures were incubated for 2 and 8 days, respectively. Coverslips were then removed and rinsed once in sterile distilled water to remove non-adherent planktonic cells. For scanning electron microscopy (SEM), L. biflexa and L. interrogans biofilms were fixed in 2.5 % glutaraldehyde/0.1 M cacodylate buffer at 4 °C for 1 h and overnight, respectively. The floating biofilm of L. biflexa was grown in 10 ml liquid EMJH medium for 72 h at 30 °C, then put on a glass coverslip, dried for 10 min at room temperature and fixed in 2.5 % glutaraldehyde/0.1 M cacodylate buffer at 4 °C for 1 h. Fixed samples were rinsed three times with 0.2 M cacodylate buffer, post-fixed with 1 % osmium tetroxide in 0.2 M cacodylate buffer for 15 min, and washed in water. Samples were treated with 0.2 % tannic acid for 20 min, rinsed with water and treated with 0.5 % osmium tetroxide in 0.2 M cacodylate buffer for 5 min; this step was done twice. Samples were gradually dehydrated in ethanol baths, desiccated and carbon evaporated. Samples were observed with a secondary electron in-lens (SEI) detector using a JEOL JSM 6700F field emission scanning electron microscope. For cryo-scanning electron microscopy, after washing coverslips in sterile water, they were submerged in liquid nitrogen, cryofractured, sublimated for 20 min at –95 °C, and metallized with chrome for 120 s. Samples were observed with a lower electron image (LEI) detector, using the above scanning electron microscope. For transmission electron microscopy (TEM), biofilms were fixed in 1.6 % glutaraldehyde/0.1 M Sorensen buffer pH 7.2 and rinsed three times for 10 min in Sorensen buffer. Biofilms were post-fixed in 1 % osmium tetroxide/0.1 M Sorensen buffer for 1 h, washed in water, dehydrated through a graded series of ethanol baths and embedded in Epon. Ultrathin sections were observed using a JEOL JEM 1010 electron microscope.
Mutagenesis in L. biflexa.
Directed mutagenesis was carried out in L. biflexa serovar Patoc strain Patoc1 as previously described (Louvel & Picardeau, 2007
). Briefly, a pGEM7Z-f+ (Promega) derivative plasmid was used for the construction of plasmids containing the genes LEPBIa2006 and LEPBIa2008. The process was as follows. PCR primers for the amplification of the spectinomycin-resistance cassette and the left and right arms of the target gene were designed and in each instance introduced a restriction endonuclease site at each end of each PCR product. The resulting three PCR products were digested with the appropriate restriction endonucleases, and ligated into the pGEM7Z-f+ derivative plasmid. The plasmid constructs delivering the inactivated allele was formed by insertion of a spectinomycin-resistance cassette between the right and left arms (
0.5 kb in length) of the target gene, introducing a partial gene deletion. These plasmids, which are not replicative in Leptospira spp., were then subjected to UV irradiation and used to deliver the inactivated alleles into L. biflexa. Spectinomycin-resistant colonies were picked and tested for allelic exchange in the target gene by PCR. By using a similar strategy, we also generated a flaB mutant (LEPBIa1589) in L. biflexa (Picardeau et al., 2001
). The complete genomic sequence of L. biflexa serovar Patoc strain Patoc1 has been deposited in GenBank under the accession numbers CP000786, CP000787 and CP000788.
| RESULTS AND DISCUSSION |
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We initially observed that, under static conditions, the pathogen L. interrogans serovar Lai strain Lai 56601 formed a halo attached to the wall of glass tubes at the air–liquid interface in approximately 10 days at 30 °C (Fig. 1
). For the saprophyte L. biflexa serovar Patoc strain Patoc1, when grown under static conditions, cells were found to strongly attach to the glass surface after 2 days. For L. biflexa, we also observed the formation of a floating pellicle at the liquid–air interface after 4–5 days' incubation (Table 1
). We therefore tested a variety of saprophytic and pathogenic strains for their ability to form biofilms attached to glass tubes or floating pellicles in nutrient-rich liquid medium in glass tubes (Table 1
). A total of 90 % of the tested strains, which belong to seven Leptospira species, exhibited the ability to form biofilms. Whereas saprophytes formed biofilms in 2–5 days, a mean of 20 days was necessary for biofilm formation by pathogens (data not shown). This is correlated with the growth rates of saprophytes and pathogens, respectively (Faine et al., 1999
). Only a minority of strains were also able to form floating biofilms. Finally, three strains did not form biofilms on glass tubes (Table 1
).
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The saprophyte L. biflexa serovar Patoc strain Patoc1 and the pathogen L. interrogans serovar Lai strain 56601 were chosen for further biofilm analysis because these strains have been well characterized and both their genomes have been sequenced (M. Picardeau, unpublished; Ren et al., 2003
).
We assessed biofilm formation under static conditions at different temperatures. In this in vitro model of biofilm formation in tubes, the temperature of incubation did not influence the development of L. biflexa biofilms, as we observed formation of similar surface-attached biofilms at 21, 30 and 37 °C. The ability to form biofilms was also assessed in a low-nutrient environment (see Methods). Again, L. biflexa was observed to form biofilms in glass tubes with natural mineral water. However, the strain showed a delay in biofilm production, which correlated with slower growth in comparison to growth in EMJH medium (data not shown).
For L. interrogans, biofilms were only observed at 30 and 37 °C, but bacterial growth was not optimal at 21 °C (data not shown).
We also assessed biofilm formation of L. biflexa on different plastic surfaces by visual and direct microscopic examination after repeated washes. L. biflexa formed biofilms after 2 days growth not only on polystyrene plates (Fig. 1B
), but also on polyolefin polymers (data not shown). Although we observed slight adherence of L. interrogans to polystyrene flasks and plates, biofilms were not resistant to washes. The fastidious growth of pathogenic leptospires may affect the rate of bacterial attachment and biofilm formation in static conditions. A continuous-culture biofilm system may be more suitable for cultivating and characterizing biofilms of pathogenic leptospires.
Microscopy analysis of biofilms on abiotic surfaces
As a first approach, we used light microscopy to study biofilm formation by L. biflexa over time. Cells were allowed to adhere to and form biofilms on glass slides and were observed by phase-contrast light microscopy at intervals. The adherence of L. biflexa and subsequent biofilm formation on a glass surface is illustrated in Fig. 2
. L. biflexa formed a dense layer on glass slides, which increased in a time-dependent manner, reaching maximal levels at 48 h. Fig. 2(C)
shows typical surface coverage of the biofilm. As documented for other biofilm-forming bacteria, the developmental process of L. biflexa biofilm formation can be characterized as a three-step process: (i) adherence of planktonic cells to the surface (Fig. 2A
), (ii) biofilm maturation (Fig. 2C
), and (iii) complete or partial disintegration of the biofilm (Fig. 2E
). The microscopic aspect of the pellicular biofilm resembles the biofilm attached to a glass surface (Fig. 2
). L. biflexa cells form denser biofilms at the air–liquid interface than below this interface (Fig. 2
). This is probably due to the fact that leptospires are motile and obligate aerobic spirochaetes.
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Quantification of biofilm formation
Biofilm formation can be quantified by crystal violet staining of the cells attached to the surface. In the present study, we showed that 12-well polystyrene plates yielded the largest amount of surface-attached biomass for L. biflexa (Fig. 1B
). In light of these results, we assayed biofilm formation of L. biflexa in polystyrene plates at 30 °C under static conditions. In this assay, biomass was formed at the bottom of the wells and at the liquid–air interface (data not shown), and crystal violet staining reached a maximal A600 of approximately 2 after 2 days. Afterwards, the crystal violet staining became lower and A600 values were low as soon as 72 h incubation (Fig. 6
). The increase in crystal violet staining and biofilm production was correlated with bacterial growth in the medium and ceased in the stationary growth phase.
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We recently identified transposon mutants of L. biflexa that were not able to use some iron sources for survival (Louvel et al., 2005
, 2006
). Using transposon mutagenesis, we could also screen a library of random mutants in a polystyrene plate assay to identify biofilm-defective mutants.
Role of biofilm formation in Leptospira spp.
Bacterial biofilms have a structurally complex and dynamic architecture and can develop on many surfaces. Both saprophytic and pathogenic Leptospira strains were found to form surface-associated biofilms in standing cultures. The progression of biofilm formation by Leptospira spp. mimics other biofilms described in the literature, beginning with individual bacteria adhering to the abiotic surface, expansion into colonies, and formation of a three-dimensional structure (Hall-Stoodley et al., 2004
).
Our data, based on SEM and TEM, show differences in biofilm architecture between a strain of the pathogen L. interrogans serovar Lai and a strain of the saprophyte L. biflexa serovar Patoc in the tested conditions. This may be correlated with phylogenetic and lifestyle differences between pathogenic and saprophytic strains. L. interrogans is an important animal and human pathogen, but it was not previously considered as a biofilm-building species. Our study revealed that the majority of pathogenic strains produced detectable biofilms on abiotic surfaces in vitro. Bacteria in biofilms exhibit properties distinct from those of planktonic cells, such as increased resistance to biocides and antimicrobial agents (Hall-Stoodley et al., 2004
). Multi-species biofilms may also contribute to gene transfer between micro-organisms (Wang et al., 2002
). It was recently shown that severe leptospirosis was associated with exposure to a high concentration of leptospires in environmental water samples (Ganoza et al., 2006
). Biofilm formation may contribute to long-term survival in environmental water (Trueba et al., 2004
). In our study, natural mineral water was also used as the sole source of nutrient supply to allow the development of L. biflexa biofilms. The ability of pathogenic Leptospira to survive in aquatic ecosystems in biofilms could be one of the main factors controlling environmental survival and disease transmission. Since the long-term colonization of proximal renal tubules of mammalian maintenance host species by pathogenic leptospires is believed to proceed via the formation of cell aggregates (A. I. Ko, unpublished data), biofilm formation may also play an important role in maintaining chronic carriage of the pathogen L. interrogans in animal reservoirs. The determination of the structure and the mechanism of colonization of kidneys in the animal reservoir will no doubt be of fundamental importance.
Further studies are required to study the biofilms of these ubiquitous organisms in the context of their environmental habitats such as fresh water or renal tubules.
| ACKNOWLEDGEMENTS |
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Edited by: G. E. Duhamel
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Received 7 November 2007;
revised 14 December 2007;
accepted 17 February 2008.
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