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Antimicrobial Agents and Chemotherapy, July 2008, p. 2626-2631, Vol. 52, No. 7
0066-4804/08/$08.00+0 doi:10.1128/AAC.01666-07
Copyright © 2008, American Society for Microbiology. All Rights Reserved.

Institute of Dental Sciences, Faculty of Dental Medicine, Hebrew University—Hadassah, Jerusalem, Israel,1 Department of Prosthodontics, Faculty of Dental Medicine, Hebrew University—Hadassah, Jerusalem, Israel,2 School of Dentistry, University of California San Francisco, San Francisco, California3
Received 25 December 2007/ Returned for modification 4 February 2008/ Accepted 25 February 2008
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Interestingly, the use of light to kill bacteria growing on agar surfaces appears to be more effective than when they are grown in suspension (6). This is probably attributable to the scattering and absorption of light in the suspension, reducing penetration depth. Visible light wavelengths, mostly in the presence of a chemical photosensitizer, have been studied as a potential means of affecting bacterial vitality (6, 11, 16, 17, 23, 24, 34, 35, 39). Photosensitizers, molecules that are chemically excited by light of specific wavelengths, may cause biological damage or lead to the generation of reactive oxygen species (ROS) capable of reacting and affecting biological systems such as organelles, cells, and bacteria. More than 400 compounds are known to display photosensitizing properties. Most of them are dyes, drugs, and natural substances. Although many of these dyes may have inherent antibacterial effects, it is generally only during irradiation that the photodynamic bactericidal effect is elicited (20).
Recently, a synergistic antibacterial effect of noncoherent blue light, often used in restorative dentistry, and hydrogen peroxide (H2O2) on S. mutans under planktonic conditions was observed (5). Due to the widespread use of antibiotics and the emergence of more resistant and virulent strains of microorganisms, there is an urgent need to develop alternative sterilization technologies that affect biofilms. The aim of this study was to explore the synergistic effect of noncoherent blue light and H2O2 on bacterial viability and the effect of such treatment on gene expression of S. mutans in biofilm.
(This study is part of the Ph.D. thesis of D. Moreinos.)
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Light source. A xenon lamp with a combined filter for the transmission of noncoherent blue light (wavelengths of 400 to 500 nm; MSqCaesarea1, Israel) was used. The distance between the light source tip and the exposed sample was set at 1.5 cm in order to obtain a constant power density of 1.14 W/cm2. An average light power of 440 mW was measured with a power meter (Ophir, Jerusalem, Israel) over a spot 0.7 cm in diameter. The calculated power density was obtained by dividing the average power by the light-exposed area.
Bacterial biofilm formation. Biofilms were formed on a 96-well microplate by a method similar to that described by Nobbs et al. in 2007 (22). Briefly; S. mutans UA 159 cells were grown in brain heart infusion broth (BHI; Acumedia Manufacturers, Baltimore, MD) and incubated under aerobic conditions at 37°C in 5% CO2. All bacteria were subcultured at least twice before biofilm growth. A 20-µl volume of a bacterial culture grown overnight, 180 µl of BHI, and sucrose at a final concentration of 4% were placed in wells of a 96-well microplate (Nunc, Roskilde, Denmark). The plate was then incubated for 24 h, in the course of which biofilm was formed. After biofilm formation, the wells were washed with PBS to remove loosely bound bacteria.
Bacterial viability: microbial assays. Bacterial biofilm samples in the presence of 3, 30, and 300 mM H2O2 were exposed to noncoherent blue light for 30 and 60 s, which is equivalent to 34 and 68 J/cm2, respectively. Following light exposure, the samples were washed twice with PBS, followed by the addition of 200 µl PBS to each well. The immobilized bacteria were then separated from the wells with two pulses of 2 s each from a probe sonicator (Vibracell; Sonics and Materials, Newtown, CT) (33). The samples were serially diluted (10–2 to 10–7) in sterile PBS and then applied to mitis salivarius supplemented with tellurite-bacitracin agar plates (9). The number of viable bacteria was determined by counting the CFU on the plates after 48 h of incubation at 37°C with 5% CO2. All experiments were conducted in triplicate and repeated six times (n = 18). Control groups consisted of samples undergoing the same procedure except that they were only exposed to light without H2O2 or to H2O2 at the different concentrations with no light exposure.
A synergistic, additive, or antagonist effect of H2O2 and light exposure was determined as follows. The minimum inhibitory dose (MID) of light exposure and the MIC of H2O2 required to inhibit bacterial growth (at least at a magnitude of 99%) were examined separately. Synergistic, antagonistic, or additive effects of light and H2O2 were determined by calculating the fraction inhibitory concentration index (FIC) as follows: FIC = Antibacterial agent(MIC) in combination with light exposure(MID)/Antibacterial agent(MIC) + Antibacterial agent(MIC) in combination with light exposure(MID)/Light exposure(MID). An index lower than 0.5 indicates that a synergistic effect has taken place. An index higher than 4 indicates an antagonist effect (10, 13).
Tests similar to those described above were performed on planktonic bacteria in order to compare the combined light and H2O2 effects on immobilized and planktonic bacteria. Briefly, S. mutans bacteria were grown as described above. A 50-µl volume of bacteria suspended in PBS was placed in wells of a 96-well microplate. H2O2, at a final concentration of 30 mM, was added to each well, and the samples were exposed to the light source. The samples were then immediately diluted to 10–2 to 10–7 and plated, and the CFU were counted. Each plate also contained control samples of 30 mM H2O2 with and without exposure to light. The effect of light combined with H2O2 on bacteria in biofilm was measured as described above. All experiments were performed in triplicate and repeated four times (n = 12).
Bacterial viability: confocal scanning laser microscopy. Bacterial biofilm samples treated with a combination of 30 mM H2O2 and 60 s (equivalent to 68 J/cm2) of light exposure and untreated control samples were incubated for an additional 6 h and stained with a live/dead BacLight bacterial viability kit (Molecular Probes Inc., Eugene, OR). The stains were prepared in accordance with the manufacturer's instructions. In short, 2 µl of each stain was dissolved in 96 µl of double-distilled water and 30 µl of the stain solution was added to each well. The microplates were incubated at room temperature in the dark for 20 min. Incubation samples were then washed twice with PBS and examined under a confocal scanning laser microscope (CSLM) (12).
Bacterial viability: ATP analysis.
Bacterial biofilm samples were prepared and treated with a combination of 30 mM H2O2 and noncoherent light for 60 s as described above. After incubation, the bacteria were dissociated from the wells with a probe sonicator as previously described. A 150-µl volume of the bacterial suspension was then transferred to a test tube containing 500 µl of lysis buffer, and the test tube was incubated at room temperature for 10 min. Glass beads (diameter,
160 µm; Sigma, St. Louis, MO) were added, and the cells were disrupted with a Fast Prep Cell Disrupter (Bio 101, Savant Instruments, Inc., Holbrook, NY). A 100-µl volume of the suspension was transferred to a glass test tube, and 100 µl of luciferase was added. ATP levels were determined with the aid of an ATP bioluminescence assay kit (CLS-II; Roche, Manheim, Germany). The results were normalized to those obtained with untreated control samples (30).
Gene expression. Bacterial biofilm samples were treated with a combination of 30 mM H2O2 and 60 s of light exposure (equivalent to 68 J/cm2). They were dissociated from the wells with a probe sonicator as described above. Samples were then transferred to test tubes containing 10 ml BHI and incubated at 37°C with 5% CO2 for 24 h. After incubation, 3 ml of each sample (optical density at 650 nm = 0.5) was transferred to a test tube and 3 ml of RNA protect (Qiagen, Hilden, Germany) was added to each test tube, which was then incubated at room temperature for 10 min. Cells were collected by centrifugation (4,000 rpm for 8 min at 4°C). Total RNA extraction, reverse transcription (RT)-PCR, and real-time quantitative PCR were performed as described by Shemesh et al. (28). In short, collected cells were resuspended in Tri-reagent (Sigma-Aldrich) and disrupted with a Fast Prep Cell Disrupter (Bio 101, Savant Instruments). 1-Bromo-3-chloropropane (Molecular Research Center, Cincinnati, OH) was added to the RNA-containing supernatant. The upper aqueous phase was precipitated with isopropanol. After centrifugation, the pellet was washed with ethanol and resuspended in diethyl pyrocarbonate-treated water. Residual DNA was eliminated by DNase, and the RNA was precipitated with ethanol and resuspended with diethyl pyrocarbonate-treated water. The RNA concentration was determined spectrophotometrically by measuring the A260/A280 ratio with a NanoDrop instrument (ND-1000; NanoDrop Technologies, Wilmington, DE). The integrity of the RNA was assessed by agarose gel electrophoresis. An RT reaction mixture containing random hexamers, a deoxynucleoside triphosphate mixture, and a total RNA sample was incubated to remove any secondary structure. RT buffer, MgCl2, dithiothreitol, RNaseOUT recombinant RNase inhibitor, and Super Script II RT (Invitrogen, Life Technologies, Carlsbad, CA) were added to each reaction mixture. After incubation, the reaction was terminated and the cDNA samples were stored at –20°C until used. Real-time quantitative PCR was performed with a GeneAmp 7000 Sequence Detection System (PE Applied Biosystems, Foster City, CA) with SYBR green PCR Master Mix (PE Applied Biosystems). The reaction mixture contained the cDNA sample and the appropriate PCR primer (Table 1). The cycle profile was as follows: 1 cycle of 50°C for 2 min, 1 cycle of 95°C for 1 min, and 30 cycles of 95°C for 15 s and 60°C for 1 min. After the last cycle, the following dissociation protocol was followed: a hold at 95°C for 15 s, a hold at 60°C for 20 s, and a slow ramp (20 min) from 60 to 95°C. The critical threshold cycle (CT) is defined as the cycle at which fluorescence is detectable above the background and is inversely proportional to the logarithm of the initial number of template molecules. A standard curve was plotted for each primer set with CT values obtained by the amplification of known quantities of cDNA from S. mutans MT8148. The standard curves were used for transformation of the CT values to the relative number of cDNA molecules. The data are expressed as the mean ± the standard deviation of triplicate experiments. In this study, we examined the differential expression of several genes associated with biofilm formation, i.e., ftf, gtfB, comDE, relA, brp, and smu630 (Table 1). The expression levels of all tested genes were normalized using the 16S rRNA as internal standard.
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TABLE 1. Genes tested, their biological functions, and primers used
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FIG. 1. Bacterial growth following exposure of bacterial biofilm to noncoherent visible light (at wavelengths of 400 to 500 nm) in combination with different concentrations of H2O2. The growth of nonexposed (control) bacterial samples and samples exposed to light for 30 s (equivalent to 34 J/cm2) or 60 s (equivalent to 68 J/cm2) in the absence or presence of H2O2 at a concentration of 3, 30, or 300 mM is expressed as CFU counts on a logarithmic scale. Asterisks indicate statistically significant differences (P < 0.001).
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Effect of noncoherent light and H2O2 on planktonic bacteria versus that on bacteria in biofilm. The combined effects of noncoherent light and 30 mM H2O2 on bacteria in biofilm and under planktonic conditions were further compared in relation to the untreated control samples. Bacteria under planktonic conditions showed CFU count reductions of 0.72 and 1.19 logs after light exposure for 30 and 60 s, respectively. Bacteria in biofilm showed greater CFU count reductions of 2.12 and 2.6 logs after light exposure for 30 and 60 s, respectively (Fig. 2) (P < 0.02).
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FIG. 2. Comparison of the number of CFU under planktonic conditions and in biofilm of nonexposed (control) bacterial samples and samples exposed to light for 30 s (equivalent to 34 J/cm2) or 60 s (equivalent to 68 J/cm2) in the presence of 30 mM H2O2. A statistically significant difference between the biofilm and planktonic groups was found (P < 0.02).
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FIG. 3. CSLM images of different layers, from the biofilm surface (left upper image) to the deepest layer of the biofilm (right lower image). All samples were exposed to noncoherent visible light (at wavelengths of 400 to 500 nm) for 60 s (equivalent to 68 J/cm2) in the presence of 30 mM H2O2. Panels: a, immediately after exposure; b, 3 h after exposure; c, 6 h after exposure. Green indicates live bacteria, red indicates dead bacteria, and yellow indicates the presence of both live and dead bacteria.
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FIG. 4. Bacterial ATP levels measured before (zero time) and at different time points after exposure to noncoherent visible light (at wavelengths of 400 to 500 nm) for 60 s (equivalent to 68 J/cm2) in the presence of 30 mM H2O2, H2O2 alone, and light exposure alone. There was a statistically significant difference in ATP levels at 0.2, 3, and 6 h after combined irradiation and H2O2 treatment (P < 0.001) (no significant difference was found after 1 h).
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FIG. 5. Relative expression of several genes related to biofilm formation 24 h after treatment of bacterial biofilm by exposure to noncoherent visible light (at wavelengths of 400 to 500 nm) for 60 s (equivalent to 68 J/cm2) in the absence (horizontal lines) or presence (vertical lines) of 30 mM H2O2 or to 30 mM H2O2 alone (white columns) and in a nontreated control (black columns). All samples were normalized to the endogenous 16S rRNA. The expression of all genes was significantly enhanced following treatment, except for ftf and relA (P < 0.05).
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Previous findings demonstrated the mutual antibacterial effect of noncoherent light and H2O2 on planktonic oral bacteria (5). Since it is now well established that the virulence characteristics of bacteria can be markedly altered when they exist in biofilm, in the present study, we explored the potential synergistic effect of irradiation by noncoherent blue light and H2O2 on S. mutans embedded in biofilm. The results show that noncoherent blue light alone at fluences of up to 68 J/cm2 had a limited effect on S. mutans viability in biofilm, as did H2O2 at concentrations of up to 300 mM. However, a dose-dependent synergistic antibacterial effect on bacteria embedded in biofilm was demonstrated when noncoherent blue light and H2O2 were applied simultaneously. It was previously shown that the phototoxic effect of noncoherent blue light on planktonic bacteria involves the formation of ROS and that hydroxyl radicals (OH.) play an important role in this process (4, 5). It is assumed that the synergistic effect on bacterial vitality in biofilm is the result not of direct fission of H2O2 by light, as described for the mechanism of action of UV light, but of the generation of the highly reactive OH. radical when H2O2 encounters "free Fe(II)," via the Fenton reaction (5).
The OH. radical is a potent oxidant that can react readily with macromolecules such as DNA or lipids in the cell membrane. However, penetration of the cell wall by H2O2 may be the rate-limiting factor in its antibacterial activity (1). Wood et al. (39) showed that the antibacterial effect of white light combined with photosensitizers is directly associated with the age of the biofilm and its architecture. Using lethal photosensitization, Williams et al. (34) found that the antibacterial effect of red light, in combination with the photosensitizer toluidine blue O, on S. mutans embedded in collagen was less than that obtained for planktonic suspensions. Using a Q-switched ruby laser, Soukos et al. (29) showed that photomechanical energy enhanced the penetration into a biofilm of the oral pathogen Actinomyces viscosus by methylene blue.
As limitation of diffusion into deep layers of the biofilm is one of the main problems in affecting bacteria, alternative means of light and sound energy have been used to overcome this obstacle. Our assumption was that light energy together with small molecules such as H2O2 would be capable of affecting bacteria in deeper layers of the biofilm. The combination of noncoherent light and H2O2 may also induce disruption of the biofilm by photo-oxidation along the light path, allowing greater permeation of the interbacterial void volume of the biofilm by H2O2 and eventually also of the cells. This increase in the local concentration of H2O2 in the microenvironment of the biofilm, and the fact that H2O2 molecules are small compared with the photosensitizer molecules, may explain the antibacterial activity observed in the deep layers of the biofilm.
Although it appears that the combination of H2O2 and noncoherent light has an advantage in penetrating the deep layers of the biofilm, its kinetics of action at those dosages and exposures is not high. Our CLSM results show that the antibacterial effect on bacteria embedded in biofilms is delayed for several hours after treatment. This observation is further supported by analysis of ATP levels. Our results clearly show a reduction in bacterial physiology expressed by ATP levels, following an increase in ATP levels immediately after light and H2O2 treatment. Visible light exposure in the presence of H2O2 resulted in accumulation of ROS in the bacterial surroundings. We assume that such a change creates environmental conditions stressful to the exposed bacteria. In response, the bacteria adapt by enhanced production of ATP. When these attempts fail, the number of live bacteria is reduced and the total amount of ATP in the sample is reduced gradually over time.
CLSM images indicate that the antibacterial effect begins in the middle layers of the biofilm (35 to 65 µm) and spreads to the remaining layers over a period of several hours. It is likely that the heterogeneity of cell vitality through biofilms is due to nutrient and/or physicochemical (e.g., pH, redox potential) gradients and subsequent limitation (38). Here, the depth-related vitality profile could be explained by ROS formation, which does not take place under anaerobic conditions such as those existing in the deepest layers of the biofilm. In the upper layers, the ROS that do form following 60 s of light treatment are either washed out by PBS or react with the air surrounding the wells and are neutralized before they can react with the bacteria, similar to the "oxygen inhibition layer" phenomenon, referred to as an unpolymerized surface layer observed when using blue light in room air to cure resins used for restorative dentistry (25). This phenomenon is not in agreement with another study, where lethal photosensitization occurred predominantly in the outermost layers of the biofilm (40). However, unlike our study the S. mutans biofilms in that study were exposed to larger and less diffusible molecules of toluidine blue O in combination with red light for longer periods of time (5 to 30 min).
Light has been shown to affect the regulation of gene expression. It may decrease gene expression (8) or induce regulation (26), depending on the environmental conditions and type of microorganism. Intriguing is the fact that a combination of noncoherent light irradiation and H2O2 results in the up-regulation of several genes of S. mutans, especially some that are associated with biofilm formation. The gtfB gene, which encodes the GTF enzyme that synthesizes the extracellular glucans which play a pivotal role in sucrose-dependent bacterial adhesion, is highly up-regulated in the presence of light and H2O2. These findings suggest that the combination of light and H2O2 has a great potential to enhance bacterial adhesion. However, it should be noted that sucrose is required as a substrate for GTF activity to synthesize those glucans. On the other hand, the combination of noncoherent light irradiation and H2O2 does not alter mRNA levels of ftf, which encodes the fructosyltransferase enzyme that synthesizes extracellular fructans. The different effects on gtf and ftf indicate that the influence of noncoherent light in combination with H2O2 is of a specific nature. brp, which is a regulatory gene responsible for biofilm formation, and smu630, which is associated with biofilm formation, are also up-regulated, indicating again the potential of combined noncoherent light and H2O2 to induce biofilm formation. comDE, which encodes a histidine kinase receptor (comD) and a cognate response regulator (comE) of the competence-stimulating peptide, which are part of the quorum-sensing cascade of S. mutans (32), is up-regulated too. This effect may enhance the ability of the bacteria to form biofilm if other environmental conditions are adequate. On the other hand, relA, which is associated with bacterial physiology by acting as a guanosine tetra (penta)-phosphate synthetase, is not significantly affected by noncoherent light and H2O2. As the genes tested are only selected genes of the S. mutans genome, additional investigation of other genes which are associated with biofilm formation, inhibition, or quorum sensing may further elucidate the broader spectrum of effects of the combined therapy on biofilm formation and bacterial physiology.
Overall, our results are in agreement with those of Khaengraeng and Reed (14), who suggested that the sublethal damage to bacterial cells caused by light leads to an ROS-sensitive state since it imposes an additional stress on the bacteria. Affecting bacteria in biofilm is one of the greatest challenges in the prevention and treatment of infectious diseases such as those associated with dental biofilm. This study presents a potential new means to beneficially alter oral biofilm: a synergistic effect obtained by the simultaneous harnessing of noncoherent blue light and H2O2.
Published ahead of print on 3 March 2008. ![]()
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