Journal of Antimicrobial Chemotherapy (2006) 57, 872–876 doi:10.1093/jac/dkl070 Advance Access publication 13 March 2006 Synergic antibacterial effect between visible light and hydrogen peroxide on Streptococcus mutans Osnat Feuerstein1*, Daniel Moreinos1,2 and Doron Steinberg2 1 Department of Prosthodontics, Hebrew University–Hadassah School of Dental Medicine, Jerusalem, Israel; Institute of Dental Sciences, Hebrew University–Hadassah School of Dental Medicine, Jerusalem, Israel 2 Received 30 November 2005; returned 19 January 2006; revised 9 February 2006; accepted 14 February 2006 Objectives: To evaluate the possibility of enhancing the phototoxic effect on Streptococcus mutans using a potentially antibacterial synergic effect between blue light and hydrogen peroxide (H2O2), and to investigate the antibacterial mechanism involved. Methods: Growth of S. mutans samples was determined after exposure to light in the presence and absence of H2O2. The effect of such light on H2O2 degradation, on reactive oxygen species (ROS) generation and on the exposed-medium temperature was examined. Results: The combination of light exposure for 20 s (23 J/cm2) and a concentration of 0.3 mM H2O2 yielded 96% growth inhibition, whereas, when applied separately, light exposure decreased bacterial growth by 3% and H2O2 by 30% compared with the control. The results showed no direct effect of the light on H2O2 degradation, a partial protective effect of ROS scavengers on S. mutans and a non-lethal increase in the medium temperature after light exposure. Conclusions: An antibacterial synergic effect between blue light and H2O2 was observed. The mechanism of the phototoxic effect on S. mutans was basically a photochemical process, in which ROS were involved. Application of such light in combination with H2O2 to an infected tooth could be an alternative to or serve as an additional minimally invasive antibacterial treatment. Keywords: light exposure, phototoxic effect, reactive oxygen species Introduction There is no dispute that topical antibacterial agents commonly used in dentistry have a potential bactericidal effect on oral bacteria. However, most agents have undesired side effects, which can be minimized by reducing their concentration. The synergic effect of certain antibacterial agents may enable their concentration to be reduced without affecting their biological activity.1–3 Conventional synergy is achieved by a combination of two chemical antibacterial agents. The use of a chemical photosensitizer agent in conjunction with lethal light photosensitization has been shown to be effective against bacteria.4–9 However, photosensitizers have the disadvantages of possibly colouring the surrounding tissues and of low availability. Hydrogen peroxide (H2O2) and near-ultraviolet (UV) radiation is another combination of chemical agent and light that may enhance the damaging effect on microorganisms.10 This effect may be explained by OH· production, from homolytic fission of the H2O2 caused by UV light. This phenomenon has not yet been investigated using visible light. Blue non-coherent light sources, such as the plasma-arc curing (PAC) light, the halogen lamp and the light emitting diode, are often used in dentistry for photocuring resin composites. Previous studies have shown that visible light at wavelengths of 400– 500 nm (blue light) induced an oxygen-dependent phototoxic effect on the periopathogenic bacteria Porphyromonas gingivalis11–13 and Fusobacterium nucleatum, in which reactive oxygen species (ROS) such as hydroxyl radicals (OH·) were involved.12 These ROS have been shown to cause damage to proteins, lipids and nucleic acids.14,15 Indeed, although nonionizing, visible light (wavelengths 408–750 nm) causes mutagenic and metabolic damage to Escherichia coli cells.16 In a recent study we found that the phototoxic effect of blue light on Streptococcus mutans, which is associated with dental caries, was lower than that on P. gingivalis and F. nucleatum.11 ............................................................................................................................................................................................................................................................................................................................................................................................................................. *Corresponding author. Tel: +972-2-6776142; Fax: +972-2-6429683; E-mail: [email protected] ............................................................................................................................................................................................................................................................................................................................................................................................................................. 872 The Author 2006. Published by Oxford University Press on behalf of the British Society for Antimicrobial Chemotherapy. All rights reserved. For Permissions, please e-mail: [email protected] Antibacterial synergy of H2O2 and visible light This is probably related to the fact that S. mutans is protected by antioxidant defence enzymes such as superoxide dismutase (SOD).17 The aim of the present study was to evaluate the possibility of enhancing the relatively low phototoxic effect on S. mutans by making use of a potentially antibacterial synergic effect between blue light and H2O2, and to investigate the mechanism involved. Materials and methods Bacteria S. mutans (ATCC 27351) was used in these experiments. The bacteria were grown in brain heart infusion (BHI) broth (Acumedia Manufacturers, Baltimore, MD, USA) and incubated at 37 C in 5% CO2. All bacteria were subcultured at least twice before exposure to light. The bacteria were then suspended in PBS (Sigma, Steinheim, Germany), and a 50 mL suspension was placed in the wells of a 96well microplate. Hydrogen peroxide (H2O2) Before exposure to light, 50 mL of H2O2 was added to each well, at the following final concentrations: 30 mM, 3 mM and 0.3 mM. Control bacterial samples, in the absence of H2O2, were prepared with the addition of 50 mL of PBS. The H2O2 concentrations used were significantly lower than the MIC. Light source A xenon lamp with a combined filter for transmission of blue light (450–490 nm) (MSq, Caesarea, Israel), the dental PAC light, was applied. The distance between the light source tip and the exposed sample was fixed to obtain a constant power density. An average light power of 440 mW was measured using a power meter (Ophir, Jerusalem, Israel) over a spot of 0.7 cm diameter. To calculate power density, the average power was divided by the area of the light spot. Effect of light exposure in combination with H2O2 on bacterial growth The bacterial samples (100 mL) in the presence and absence of H2O2 were exposed to blue light with a power density of 1144 mW/cm2 for 20, 30 and 40 s and 10 min, equivalent to 23, 34, 46 and 686 J/cm2. Following light exposure, 100 mL of BHI at twice the normal concentration was added to each well. The experiment was conducted at room temperature under aerobic conditions, and the samples were then immediately incubated for 24 h at 37 C in 5% CO2. Bacterial growth was determined by measuring the optical density at OD650 of each sample using a microplate reader (VERSAmax, Molecular Devices, Sunnyvale, CA, USA). All experiments were conducted in triplicate and repeated four times (n = 12). To determine the synergic, additive or antagonist effect between H2O2 and the light source, the minimal inhibitory dose (MID, i.e. the minimum level of light exposure required to inhibit 90% of bacterial growth) and the MIC of H2O2 were determined. The MIC of H2O2, when applied separately, was established using a broth dilution method similar to that described by Shani et al.18 Then, the fractional inhibitory concentration index (FICI) was calculated, based on the formula described by Giertsen et al.,19 as follows: FICI = H2O2 (MIC) (in combination with light exposure)/H2O2 (MIC) + Light exposure (MID) (in combination with H2O2)/Light exposure (MID) An index value lower than 1.0 indicates that a synergic effect has taken place. An index value equal to 1.0 indicates an additive effect. An index value higher than 1.0 indicates an antagonistic effect between H2O2 and the light exposure. Direct effect of blue light on H2O2 degradation The following experiment was performed to determine whether blue light affects the homolytic fission of H2O2, which results in the formation of ROS. The degradation of H2O2 is enhanced in vivo in the presence of trace amounts of transition metals. Samples (100 mL) containing H2O2 to which a cocktail of three transition metals (cupric chloride, ammonium ferrous sulphate and manganese chloride at final concentrations of 10 mM each), PBS or double distilled water was added were placed in a 96-well microplate. Experimental samples were exposed to blue light for 60 s, whereas control samples were not exposed. The concentration of H2O2 in each sample was measured using a modification of the ferrithiocyanate method described by Thurman et al.20 Briefly, after exposure to the light, 10 mL of 10 mM ferrous ammonium sulphate and subsequently 5 mL of 2.5 M potassium thiocyanate were added to each well. The absorption of the red ferrithiocyanate complex formed in the presence of H2O2 was measured at 480 nm using a microplate reader (VERSAmax, Molecular Devices, Sunnyvale, CA, USA). Effect of light on bacterial growth in the presence of scavengers This experiment was performed to determine whether generation of ROS is involved in the phototoxic effect of blue light in the absence of H2O2 on S. mutans. Before exposing bacterial suspensions to light, a cocktail containing the following ROS scavangers was added (final concentration): 20 U/mL catalase from bovine liver (Sigma, Steinheim, Germany), 100 mM dimethylthiourea (DMTU) (Sigma), 30 U/mL SOD from Escherichia coli (Sigma) and 30 mM ascorbic acid (Sigma). Samples (100 mL) were placed in a 96-well microplate and exposed to blue light at 686 J/cm2 (1144 mW/cm2 for 10 min) under aerobic conditions. Then, 100 mL of sterile broth was added to the samples and the microplate was incubated at 37 C in 5% CO2 for 24 h. Bacterial growth was determined as described above. All experiments were carried out in triplicate and repeated four times (n = 12). Temperature change following exposure to light An increase in temperature during exposure to light could affect bacterial growth. The temperature was measured in triplicate using thermocouple electrodes (Almemo, Holzkirchen, Germany) placed in 100 mL of medium (PBS) in a 96-well microplate, before and immediately after exposure to light for 20 s and 1, 2, 3, 4 and 10 min. Statistical methods To assess the effect of different combinations of H2O2 and light exposure on bacterial growth, two-way ANOVA was applied. The influence of scavengers on the effect of the light source on bacterial growth was assessed using one-way ANOVA test. The effect of exposure to the light source on the degradation of hydrogen peroxide was assessed by comparing red ferrithiocyanate complex formation between exposed and non-exposed H2O2 samples, using the t-test as well as the non-parametric Mann–Whitney test. All the applied tests were two-tailed, and a P value of £0.05 was considered statistically significant. 873 Feuerstein et al. Results Effect of blue light in combination with H2O2 on bacterial growth Bacterial growth was assessed following light exposure in combination with different concentrations of H2O2. Growth of the non-exposed (control) bacterial samples, and exposed samples in the absence and presence of H2O2, was expressed as the percentage OD650 of the control non-exposed bacterial samples in the absence of H2O2 (100%) (Figure 1). Exposure of bacterial samples to blue light in the absence of H2O2 showed no effect upon exposure for 20, 30, 40, 60 and 180 s. Only an exposure time of 10 min (686 J/cm2) caused a reduction in bacterial growth. H2O2 at a concentration of 0.3 mM decreased bacterial growth by 30% compared with the control. An exposure time of 20 s (23 J/cm2) decreased bacterial growth by 3% compared with the control. The combination of light exposure for 20 s and a concentration of 0.3 mM H2O2 yielded 96% growth inhibition compared with the control. Statistical analysis showed that H2O2 treatment, exposure to light and their interaction are responsible for 95.9% of the variability in bacterial growth (coefficient of determination R2 = 0.959). The FICI value of this combination was 0.0501, suggesting that a synergic effect had taken place. Direct effect of blue light on the degradation of H2O2 The concentration of H2O2 was determined in the non-exposed samples and in the 60 s light-exposed H2O2 samples. H2O2 concentration was essentially the same in the exposed H2O2 samples and in the control (data not shown). Effect of light on bacterial growth in the presence of scavengers Figure 2 shows the growth of the control non-exposed bacterial samples and of the light-exposed bacterial samples in the presence and absence of ROS scavengers. Bacterial growth was expressed as the percentage OD650 of the control nonexposed bacterial samples in the absence of ROS scavengers (100%). Bacterial growth after exposure to light in the presence of ROS scavengers was significantly higher than in their absence. On the other hand, a comparison between samples exposed to blue light with and without ROS scavengers showed that the presence of scavengers did not completely eliminate the bactericidal effect of the blue light (P < 0.001 one-way ANOVA). Temperature change following exposure to light and its effect on bacterial growth The bacterial medium temperature was measured before and immediately after exposure to blue light for up to 10 min. Increases in temperature of 1, 3.6, 4.6, 5.7 and 13.9 C after exposures of 20, 60, 120, 180 and 600 s, respectively, were measured when compared with the control at 25 C. There was no difference in bacterial growth between samples incubated at 40 C for 10 min and the control samples (data not shown). Discussion The results of the present study show a synergic antibacterial effect between blue light and H2O2. The combination of light exposure for 20 s (23 J/cm2) and a concentration of 0.3 mM H2O2 yielded 96% growth inhibition, whereas, when they were applied separately, bacterial growth was decreased by 3% when exposed to light and by 30% in the presence of H2O2 as compared with the control. The results do not support the assumption that most of the damage to the bacterial cells was the result of the fission of H2O2, caused by the visible light, similar to the mechanism of action of 120 Control 20 s 30 s 40 s 10 min Bacterial growth (%) 100 80 60 40 20 0 0 mM 0.3 mM 3 mM 30 mM H2O2 concentration Figure 1. Bacterial growth following exposure to blue light in combination with different concentrations of H2O2. Growth of the non-exposed (control, black) bacterial samples and the samples exposed to blue light at 1144 mW/cm2 for 20 s (horizontal lines), 30 s (vertical lines), 40 s (grey) and 10 min (white) in the absence (‘0 mM’) and presence of H2O2 at a concentration of 0.3, 3 and 30 mM, expressed as percentage OD650 of the non-exposed bacterial samples in the absence of H2O2 (100%). 874 Antibacterial synergy of H2O2 and visible light 120 Scavengers No scavengers Bacterial growth (%) 100 80 * 60 40 20 0 No exposure 10 min exposure No exposure 10 min exposure 2 Figure 2. Bacterial growth of the control non-exposed samples and of the blue-light-exposed samples (1144 mW/cm , 10 min) in the presence (black) and absence (white) of ROS scavengers. Bacterial growth is expressed as percentage OD650 of the control non-exposed bacterial samples in the absence of ROS scavengers (100%). *Significant difference between the group of samples exposed to light in the presence of scavengers and all the other groups (P < 0.001). UV light.10 However, the synergy between blue light and H2O2 might be the result of the following mechanisms: (i) Highly reactive OH· could be generated when H2O2 encounters ‘free Fe(II)’, via the Fenton reaction.10 Therefore, conditions under which bound Fe(II) is liberated, such as photooxidation, are extremely dangerous to metabolically active Fe-containing cells, not only because of the generation of OH· but also because the loss of Fe from iron-dependent enzymes leads to failure of the biochemical pathways in which they participate.21 (ii) OH·, being a potent oxidant, can react readily with macromolecules such as DNA or lipids in the cell membrane,22 a principal site of photo-oxidative damage.23 (iii) H2O2 could increase the plasma membrane permeability24 of the cells sublethally injured by exposure to light. This might also lead to a higher penetration of H2O2, resulting in damage to the intracellular organelles. Overall, these results are in agreement with Khaengraeng and Reed,25 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 these bacteria. Indeed, our results showed a partial protective effect of ROS scavengers on bacteria exposed to blue light alone, indicating that the mechanism of the phototoxic effect on S. mutans was mainly a photochemical process, in which ROS were involved. Those results regarding S. mutans are similar to the results demonstrating the effect of blue light on P. gingivalis and F. nucleatum.12 In both studies, the lack of complete protection by the scavengers could be due to their partially inefficient access to the ROS generated within the cells and their inability to scavenge the highly reactive radicals.12,26 Involvement of a photothermal process in the mechanism of the phototoxic effect on bacteria27 can be ruled out, since the increase in medium temperature following light exposure was not lethal. However, the contribution of this minimal temperature elevation to the photochemical toxic effect cannot be excluded. The study showed that only a minute amount of H2O2, which is most likely present in saliva and tissues, was required to induce the synergic antibacterial effect between light exposure and H2O2. Application of such light in combination with H2O2 to infected tooth tissue could be an alternative to or serve as an additional minimally invasive antibacterial treatment of dental caries or of root canal infection. Planktonic bacteria may exhibit properties that are different from those exhibited by biofilm bacteria.28 Therefore, testing this effect in biofilm conditions of monoculture or mixed bacterial culture is of interest as bacteria in the oral cavity are also present in biofilms attached to tooth surfaces. The safety of applications of blue light with or without the addition of H2O2, as an antibacterial treatment, should also be further investigated on various tissues and under different physiological conditions. In conclusion, this study shows a synergic antibacterial effect between exposure to blue light and H2O2, based on a photochemical mechanism in which ROS are involved. Future studies exploring the molecular level at which the bacterial cells are affected may help to elucidate this synergic mechanism. Acknowledgements This study is part of the PhD dissertation of Daniel Moreinos. This research was funded in part by The Israel Health Ministry and was performed in the Ronald E Goldstein Center for Esthetic Dentistry and Dental Materials Research, Hebrew University-Hadassah School of Dental Medicine. Transparency declarations None to declare. References 1. Ginsburg I, Kohen R. Synergistic effects among oxidants, membrane-damaging agents, fatty acids, proteinases, and xenobiotics: killing of epithelial cells and release of arachidonic acid. Inflammation 1995; 19: 101–18. 875 Feuerstein et al. 2. Drake DR, Grigsby W, Cardenzana A et al. Synergistic, growthinhibitory effects of chlorhexidine and copper combinations on Streptococcus mutans, Actinomyces viscosus, and Actinomyces naeslundii. J Dent Res 1993; 72: 524–8. 3. Steinberg D, Heling I, Daniel I et al. Antibacterial synergistic effect of chlorhexidine and hydrogen peroxide against Streptococcus sobrinus, Streptococcus faecalis and Staphylococcus aureus. J Oral Rehabil 1999; 26: 151–6. 4. Malik Z, Hanania J, Nitzan Y. Bactericidal effects of photoactivated porphyrins—an alternative approach to antimicrobial drugs. J Photochem Photobiol B 1990; 5: 281–93. 5. Okamoto H, Iwase T, Morioka T. Dye-mediated bactericidal effect of He-Ne laser irradiation on oral microorganisms. Lasers Surg Med 1992; 12: 450–8. 6. Wilson M. Photolysis of oral bacteria and its potential use in the treatment of caries and periodontal disease: a review. J Appl Bacteriol 1993; 75: 299–306. 7. Wood S, Nattress B, Kirkham J et al. An in vitro study of the use of photodynamic therapy for the treatment of natural oral plaque biofilms formed in vivo. J Photochem Photobiol B 1999; 50: 1–7. 8. O’Neill JF, Hope CK, Wilson M. Oral bacteria in multispecies biofilms can be killed by red light in the presence of toluidine blue. Lasers Surg Med 2002; 31: 86–90. 9. Soukos NS, Ximenez-Fyvie LA, Hamblin MR et al. Targeted antimicrobial photochemotherapy. Antimicrob Agents Chemother 1998; 42: 2595–601. 10. Halliwell B, Gutteridge JMC. Free Radicals in Biology and Medicine. New York: Clarendon Press, 1989. 11. Feuerstein O, Persman N, Weiss EI. Phototoxic effect of visible light on Porphyromonas gingivalis and Fusobacterium nucleatum: an in vitro study. Photochem Photobiol 2004; 80: 412–5. 12. Feuerstein O, Ginsburg I, Dayan E et al. Mechanism of visible light phototoxicity on Porphyromonas gingivalis and Fusobacterium nucleatum. Photochem Photobiol 2005; 81: 1186–9. 13. Soukos NS, Som S, Abernethy AD et al. Phototargeting oral blackpigmented bacteria. Antimicrob Agents Chemother 2005; 49: 1391–6. 14. Storz G, Tartaglia, LA, Farr SB et al. Bacterial defenses against oxidative stress. Trends Genet 1990; 6: 363–8. 15. Farr SB, Kogoma K. Oxidative stress responses in Escherichia coli and Salmonella typhimurium. Microbiol Rev 1991; 55: 561–85. 16. Webb RB, Malina MM. Mutagenesis in Escherichia coli by visible light. Science 1967; 156: 1104–5. 17. Nakayama K. Nucleotide sequence of Streptococcus mutans superoxide dismutase gene and isolation of insertion mutants. J Bacteriol 1992; 174: 4928–34. 18. Shani S, Friedman M, Steinberg D. In vitro assessment of the antimicrobial activity of a local sustained release device containing amine fluoride for the treatment of oral infectious diseases. Diagn Microbiol Infect Dis 1998; 30: 93–7. 19. Giertsen E, Scheie AA, Rolla G. Inhibition of plaque formation and plaque acidogenicity by zinc and chlorhexidine combinations. Scand J Dent Res 1988; 96: 541–50. 20. Thurman RG, Ley HG, Scholz R. Hepatic microsomal ethanol oxidation. Hydrogen peroxide formation and the role of catalase. Eur J Biochem 1972; 25: 420–30. 21. Ghosal D, Omelchenko MV, Daly MJ et al. How radiation kills cells: survival of Deinococcus radiodurans and Shewanella oneidensis under oxidative stress. FEMS Microbiol Rev 2005; 29: 361–75. 22. Block BB. Peroxygen compounds. In: Block SS, ed. Disinfection, Sterilization, and Preservation. Philadelphia: Lea & Febiger, 1991; 167. 23. Gourmelon M, Cillard J, Pommepuy M. Visible light damage to Escherichia coli in seawater: oxidative stress hypothesis. J Appl Bacteriol 1994; 77: 105–12. 24. Branco MR, Marinho HS, Cyrne L et al. Decrease of H2O2 plasma membrane permeability during adaptation to H2O2 in Saccharomyces cerevisiae. J Biol Chem 2004; 279: 6501–6. 25. Khaengraeng R, Reed RH. Oxygen and photoinactivation of Escherichia coli in UVA and sunlight: implications for solar water treatment. J Appl Microbiol 2005; 99: 39–50. 26. Hassan HM, Fridovich I. Paraquat and Escherichia coli. Mechanism of production of extracellular superoxide radical. J Biol Chem 1979; 254: 10846–52. 27. Izzo AD, Walsh JT. Light-induced modulation of Porphyromonas gingivalis growth. J Photochem Photobiol B 2004; 77: 63–9. 28. Black C, Allan I, Ford SK et al. Biofilm-specific surface properties and protein expression in oral Streptococcus sanguis. Arch Oral Biol 2004; 49: 295–304. 876
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