Photocatalysis of titanium dioxide (TiO2) substrates is primarily induced by ultraviolet light irradiation. Anion-doped TiO2 substrates were shown to exhibit photocatalytic activities under visible-light illumination, relative environmentally-friendly materials. Their anti-spore activity against Bacillus anthracis, however, remains to be investigated. We evaluated these visible-light activated photocatalysts on the reduction of anthrax spore-induced pathogenesis.
Standard plating method was used to determine the inactivation of anthrax spore by visible light-induced photocatalysis. Mouse models were further employed to investigate the suppressive effects of the photocatalysis on anthrax toxin- and spore-mediated mortality. We found that anti-spore activities of visible light illuminated nitrogen- or carbon-doped titania thin films significantly reduced viability of anthrax spores. Even though the spore-killing efficiency is only approximately 25%, our data indicate that spores from photocatalyzed groups but not untreated groups have a less survival rate after macrophage clearance. In addition, the photocatalysis could directly inactivate lethal toxin, the major virulence factor of B. anthracis. In agreement with these results, we found that the photocatalyzed spores have tenfold less potency to induce mortality in mice. These data suggest that the photocatalysis might injury the spores through inactivating spore components.
Citation: Kau J-H, Sun D-S, Huang H-H, Wong M-S, Lin H-C, Chang H-H (2009) Role of Visible Light-Activated Photocatalyst on the Reduction of Anthrax Spore-Induced Mortality in Mice. PLoS ONE 4(1): e4167. https://doi.org/10.1371/journal.pone.0004167
Editor: Stefan Bereswill, Charité-Universitätsmedizin Berlin, Germany
Received: November 18, 2008; Accepted: December 7, 2008; Published: January 9, 2009
Copyright: © 2009 Kau et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Funding: This work was supported by National Science Council of Taiwan ROC under grant no. NSC 94-2216-E-259-002, NSC 94-2120-M-259-003, NSC 95-2314-B-320-009-MY3 and 095-2811-B-320-001. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Naturally occurring anthrax is a disease acquired following contact with anthrax-infected animals or anthrax-contaminated animal products. The disease most commonly occurs in herbivores, which are infected by ingesting spores from the soil. For centuries, anthrax has caused disease in animals and, uncommonly, serious illness in humans throughout the world . Research on anthrax as a biological weapon began more than 80 years ago . Recently, the anthrax-letter attacks further evidenced this emerging terrorist threat, leading to renewed attention to the importance of prophylaxis, prevention and handling for anthrax . Treatments or agents commonly cited to inactivate anthrax spores include heat, formaldehyde, hypochlorite solutions, chlorine dioxide, and radiation . However, most of these treatments and reagents are hazardous to humans that limit their usage in public environments only after detecting the contamination sources, rather than prevention. Thus, a safer disinfection technique, which could exert a continuous antimicrobial effect in our living environment, would be highly desirable. Here, we present a visible light inducible photocatalyst which might provide a complementary and possibly alternative approach to meet this need.
Photocatalytic titanium dioxide (TiO2) substrates have been shown to eliminate organic compounds and to function as disinfectants . Upon ultraviolet (UV) light excitation, the photon energy excites valence electrons and generates pairs of electrons and holes (electron-vacancy in the valence band) that react with atmospheric water and oxygen to yield reactive oxygen species (ROS) such as hydroxyl radicals ( . OH) and superoxide anions (O2−) . Electron holes, . OH and O2− are extremely reactive and could react with cellular components and function as biocides . Since pure TiO2 photocatalyst is effective only upon irradiation by UV-light at levels that would induce serious damage to human cells, the potential applications of TiO2 substrates for use in our living environments are greatly restricted. Recently, anion-containing anatase TiO2 photocatalysts have been identified, which are activated by illumination with visible light , , offering the potential to overcome this problem . Previously, we demonstrated that nitrogen-doped TiO2 [TiO2 (N)] photocatalyst could significantly eliminate Escherichia coli and other mild pathogens . However, its antimicrobial activity and the antimicrobial mechanism against biological weapons, such as Bacillus anthracis, has not yet been reported. In this study, the anti-spore activity of TiO2 (N) photocatalysts against B. anthracis was compared with several other bacillus species including Bacillus subtilis, Bacillus thuringiensis, and Bacillus cereus. Among these bacteria, B. subtilis is broadly distributed worldwide where it mainly inhabits the upper layers of soil , ; B. thuringiensis is an insect pathogen ; and B. cereus causes broad clinical infections including local infections, septicemia, central nervous system infections, respiratory infections, endocarditis, pericarditis and food poisoning . In this study, visible light-mediated photocatalysis was found to inactive 25%–40% spores of B. subtilis, B. thuringiensis, B. cereus and B. anthracis. Even though the efficiency of bacterial-killing is less than 1 log CFU, intriguingly, animal experiment revealed that the photocatalysis reduced more than ten times potency of B. anthracis spores to induce mortality in mice. To further investigate the underlining mechanism, here we analyzed photocatalyst-mediated inactivation of anthrax lethal toxin (LT) and the survival rate of spore after the macrophage clearance in vitro.
UV-Vis absorption spectroscopic analysis
To investigate the physical properties of pure, carbon- and nitrogen- doped TiO2 films, respectively, X-ray diffraction (XRD) patterns and Raman spectra (data not shown) were obtained. Our results showed that all the films were anatase phase but the intensity of XRD and Raman peaks was slightly decreased in carbon and nitrogen doped films, indicating that the carbon/nitrogen incorporation induced decreasing crystallinity. The UV-Vis spectra of pure, carbon and nitrogen doped TiO2 films are shown in Fig. 1. The carbon and nitrogen substitution of oxygen in TiO2 caused the absorbance edge of TiO2 to shift to the higher wavelength region. The pure TiO2 film absorption edge which was at 380 nm gradually red-shifted to ∼425 nm and ∼565 nm in carbon and nitrogen doped TiO2 films, respectively. This shift in the visible region is the result of incorporation of carbon and nitrogen into the TiO2 network to form Ti-C and Ti-N bonds. Substitutional carbon or nitrogen atoms introduce new states (C2p or N2p) close to the valence band edge of TiO2 (i.e. O2p states). As a result of this the valence band edge shifts to higher energy compared with the reference TiO2 and the band gap narrows. The energy shift of the valence band depends on the overlap of carbon states and O2p states. A higher doping concentration of carbon or nitrogen results in higher energy shift due to significant overlap of carbon or nitrogen and oxygen states and this leads to a narrower band gap in the compound .
Bactericidal activities of TiO2 photocatalysts against Bacillus subtilis
Before the spore experiments, living bacteria were used to test the photocatalysis system. Since B. anthracis is a hazardous microorganism, we first used B. subtilis as a surrogate to determine the bactericidal activity of nitrogen-doped [TiO2 (N)] and carbon-doped TiO2 [TiO2 (C)]. We placed 1×104 CFU B. subtilis on different substrates including cover glass (silica, without TiO2 coating), and silica substrates coated with thin films of TiO2, TiO2 (N), and TiO2 (C). These preparations were then illuminated with visible light and the levels of surviving bacteria were quantified as previously described . We found that TiO2 (N) exhibited a significantly better performance to reduce the number of surviving B. subtilis bacteria when compared to TiO2 and TiO2 (C) (Fig. 2, **P<0.01).
Visible-light induced bactericidal activities of TiO2–related substrates against B. subtilis after illumination at 4°C. Illumination was carried out at a light density of 3×104 lux (90 mW/cm2) for either 1 or 5 min. “Without illumination” indicates experiments conducted in a dark room without illumination. **P<0.01, compared to both respective cover glass groups and without visible light illumination TiO2 (N) groups.
To obtain dose dependent and kinetic data for B. subtilis on photocatalytic substrates, we further analyzed the effects of visible-light illumination at various distances (5 cm, 10 cm, 20 cm, and with respective illumination intensities of 3×104, 1.2×103, and 3×102 lux) or at various time points (Fig. 3). The results showed that TiO2 and TiO2 (C) substrates had no detectable bacterial-killing effect, while TiO2 (N) contained significantly greater bactericidal activity, by which it induced nearly a 1 log CFU reduction under 3×104 lux visible-light illumination for 25 minutes (Fig. 3A, 3B, *P<0.05; **P<0.01, compared to respective TiO2 groups). Although prolonged illuminations tended to increase the bactericidal effect of TiO2 (C) substrates (25 min, Fig. 3B), the killing efficiency was still not statistically significant as compared with the TiO2 groups.
Dose dependent (A) and kinetic (B) analyses of the bactericidal activity of TiO2–related substrates against B. subtilis after visible light illumination were shown. Illumination was carried out either at different light densities for 25 min (A) or at a light density of 3×104 lux (90 mW/cm2) for different time periods (B). For each illumination condition, the surviving bacteria on the TiO2 groups were normalized to 100%. *P<0.05 and **P<0.01 compared to the respective TiO2 groups.
Anti-spore activities of TiO2 (N) against Bacillus species
Photocatalyst-mediated killing was performed to determine the bactericidal effect of photocatalysis on B. cereus, B. thuringiensis and B. anthracis. Compared to TiO2 thin films, we found that TiO2 (N) thin films were significantly more effective in killing the living B. cereus, B. thuringiensis and B. anthracis bacteria under visible light illumination (Fig. 4A, *P<0.05, **P<0.01).
Bacteria B. subtilis, B. thuringiensis, B. cereus and B. anthracis were placed on TiO2 and TiO2 (N) substrates, respectively. All surviving bacteria (A) or spores (B) in the TiO2 groups were normalized to 100%. The relative percentages of surviving pathogens in the TiO2 (N) groups are shown. The illumination intensity was 3×104 lux (90 mW/cm2) and the reaction time was 25 minutes. *P<0.05 and **P<0.01 compared to respective TiO2 groups.
In spore experiments, TiO2 (N) also exhibited a better anti-spore activity than TiO2 thin films, although this activity was less efficient (25–40% killing/inactivation) (Fig. 4B, *P<0.05) compared to the results obtained in living bacteria experiments (Fig. 4A).
Treatments of photocatalyzed spores and LT to mice
A mouse model was further used to investigate whether these photocatalyzed spores are less pathogenic. Before the photocatalyst experiment, we determined anthrax spore mediated mortality in mice. We found that 50% mortality required a single inoculation of 1×106 CFU anthrax spores, and the mortality reached to 100% when 7.5×106 CFU spores were used (Fig. 5A). In photocatalyst experiment, we found that visible-light induced photocatalysis on TiO2 (N) but not pure TiO2 thin-films significantly attenuated the ability of anthrax spores (1×107 CFU, before photocatalysis) to cause mortality in mice (Fig. 5B, n = 6). Notably, the mortality of mice in TiO2 (N) groups was lower than those given treatments of 1×106 CFU spores without photocatalysis [Fig. 5B, TiO2 (N), mortality 33.3%, vs. Fig. 5A, 1×106 groups, mortality 50%]. According to the killing efficiency estimated in spore-killing experiments (approximately 25%, Fig. 4B), around 7.5×106 CFU spores should be remained viable, and theoretically the mortality of mouse should have reached up to 100% (Fig. 5A, 7.5×106 CFU groups). As a result, the reduced pathogenicity of photocatalyzed spores could not be simply attributed to the reduction of viable spores. To explain this phenomenon, we hypothesized that photocatalysis on TiO2 (N) might not only eliminate 25% of the viable population but also injure the remaining spores through inactivating bacterial components. Such injuries could be resolved during germination of spores on cultural dishes but the repair process could not be accomplished in time to enable the bacteria escape from phagocytic clearance in mice. To investigate whether photocatalysis could inactivate protein components of B. anthracis, anthrax lethal toxin (LT), an example of bacterial proteins and the major virulence factor, was subjected to visible light activated photocatalysis on TiO2 and TiO2 (N) substrates. As expected, compared to untreated LT, photocatalysis of LT on TiO2 (N) but not on TiO2 substrates significantly reduced the potency of LT to induce mortality in mice (Fig. 5C). To investigate whether LT reduced its cytotoxicity after photocatalysis, a cell culture model was used. We found that LT could induce significant cell death of macrophage J774A.1 cells before but not after being subjected to TiO2 (N)-mediated photocatalysis (Fig. 6A, **P<0.01). Western blot analysis revealed that the intact forms of both purified lethal factor (LF) and protective antigen (PA) molecules, two components of LT , , did not decrease after photocatalysis (Fig. 6B). These data might suggest that protein degradation dose not play major role in the inactivation of LT.
Mortality of C57BL/6J mice after intravenous injection of different doses (0 to 1×107 CFU) of B. anthracis spores within one-week interval is revealed (A) (n = 8). Aliquots of B. anthracis spores (1×107 CFU) was subjected to photocatalysis on TiO2 and TiO2 (N) photocatalysts, respectively; spores in TiO2 (N) groups induced less mortality in mice (△) compared to untreated (○) or TiO2 (▾) groups (B) (n = 6). Aliquots of anthrax LT (500 µg PA : LF = 5∶1) was subjected to photocatalysis on TiO2 and TiO2 (N) photocatalysts, respectively; LT (100 µg/g) in TiO2 (N) groups (△) induced less mortality in mice compared to untreated (○) or TiO2 (▾) groups (C) (n = 6).
Macrophage J774A.1 cells were subjected to LT treatments for three hours, surviving cells of untreated groups were adjusted to 100% (A). Columns designated TiO2 or TiO2 (N) represent that LT was pretreated with photocatalysis on TiO2 or TiO2 (N) substrates, respectively, before treated to J774A.1 cells. Columns designated “+L” or “−L” represent experimental conditions with or without light illumination, respectively. **P<0.01, compared to LT, TiO2-L and TiO2 (N)+L groups (A). Western blot measurements of intact LF and PA levels (arrows) of purified LT before and after visible light induced photocatalysis; band intensities of individual LF and PA samples are shown, and respective untreated groups were normalized to 100% (B).
In vitro phagocytic clearance analysis
Anthrax spore can multiply in phagocytes . To investigate whether photocatalysis might injure the spores and make them vulnerable for the clearance by phagocytes and further handicapped the bacterial amplification within phagocytes, photocatalyzed anthrax spores were then treated to macrophage J774A.1 cells. We found that spores in light illuminated-TiO2 (N) groups were not significantly multiplied in phagocytes within 24 hours (Fig. 7A, TiO2 (N)+L 1 hr vs. 24 hr). By contrast, untreated spores, or spores from groups without light illumination, or spores from illuminated-TiO2 groups were all significantly multiplied 3–4 fold within 24 hours (Fig. 7A, untreated/TiO2-L/TiO2 (N)-L/TiO2+L, 1 hr vs. 24 hr, *P<0.05, **P<0.01). Since low level of surviving bacteria in the 24-hour groups might be also possible attributed to the low phagocytic efficiency, to investigate whether photocatalysis might make these spores hard to be engulfed by phagocytes, we analyzed the remaining viable spores in the macrophage-culture medium. We found that the viable spores in the medium showed no significantly differences between each groups (Fig. 7B, 1 hr vs. 2 hr, 3 hr and 24 hr, all groups compared to each other), indicating that the low level of surviving bacteria in the TiO2 (N)+L/24 hr groups is not attributed to the low phagocytic efficiency (Fig. 7A). These results suggest that visible-light induced photocatalysis on TiO2 (N) substrates handicapped the amplification of anthrax in phagocytes.
Anthrax spores were treated to J774A.1 macrophage cells (MOI: 0.01 spores/cell). Surviving bacteria (CFU) that harvested from macrophage cell lysate (A) or macrophage cell cultural medium (B) were shown. Columns designated TiO2 or TiO2 (N) represent anthrax spores were pretreated with photocatalysis on TiO2 and TiO2 (N) substrates, respectively. Columns designated “+L” or “−L” represent experimental conditions with or without light illumination, respectively. *P<0.05, **P<0.01, compared to 1 hr groups of respective conditions (A).
The antibacterial property of photocatalysts was primarily induced under UV irradiation , , , and more recently by visible-light illuminated conditions , –. These studies provide valuable observations for the bactericidal activity of photocatalysts. Since these researches were mainly using laboratory E. coli strains as experimental materials, the potential application to apply on the eradication of spores of pathogenic bacteria, and especially the capability and the mechanism to reduce their pathogenicity were rarely discussed. Here we used spore forming bacillus bacteria as model systems to study the anti-spore activity of the visible-light photocatalyst. Since B. anthracis is a hazardous microorganism, in this study we first used B. subtilis, a bacillus bacterium with natural habitat in the soil that is not harmful to humans, as a surrogate for B. anthracis. We found that TiO2 (N) exerted anti-spore effects against B. subtilis and all our tested Bacillus species including B. cereus, B. thuringiensis and B. anthracis, with similar killing-efficiencies among these bacteria. These results suggest that B. subtilis, B. cereus, B. thuringiensis might be useful as surrogates for further photocatalyst-mediated anti-anthrax research. Even though the spore-killing efficiency is not good enough as compared with other well-developed methods , the contrast between the low spore-killing and a relatively high reduction of pathogenicity, inspired us to further investigate the underlining mechanism, by which it led us to find that the photocatalysis could inactivate the LT and handicapped the spore to multiply in the phagocytes. This is a finding not yet been reported previously.
The molecular target of photocatalyst-induced damage on bacteria is rarely discussed. It is shown that bacterial membrane lipid components likely to be the cellular target of photocatalyst induced ROS . Using living E. coli as a model system, the authors found that TiO2-mediated photocatalysis promoted peroxidation of the polyunsaturated phospholipid component of bacterial membranes and then further led to respiratory activity loss and cell death . Unlike vegetative cells, spores contain strong resistance to almost all antibacterial agents , , , as first observed by Koch over 100 years ago that B. anthracis spores could survive boiling. In the century that followed, it was learned that the protein components involving not only the composition of high density spore coat, a multilayered structure surrounding the spore that attributed to the resistance, but also the sensing responses to the renewed presence of nutrients in the environment, the condition under which the spore can convert to a growing cell through a process called germination , , . Thus, the inactivation of a spore might be not just by disrupting the lipid components; deteriorated protein function could be involved as well. Photocatalysis-mediated protein dysfunction is rarely discussed. Evidence from enzyme-linked immunosorbent assays (ELISA) indicates that photocatalysis could affect the antigenic property of hepatitis B virus surface antigen and reduce its binding to specific antibody . In this present study, we demonstrate the first time that photocatalysis could inactivate the bacterial exotoxin LT efficiently. Anthrax LT is a major virulence factor beneficial for the bacterium to establish initial infections in macrophages , . Our Western blotting analysis revealed that both PA and LF, two components of LT, remained intact after photoreactions, indicating protein degradation does not play a major role in the inactivation. Although evidences indicate that LT is not expressed in anthrax spores , , since both protein toxin and spores are sensitive to photocatalysis, it seems likely that some of the spore proteins might be also sensitive to the photoreactions. Further investigation to identify the specific protein is needed.
Taken together, this study demonstrated that TiO2 (N) substrates could inactivate both spores and toxin of B. anthracis under illumination by ordinary light sources such as incandescent lamps. Our results suggest that the suppressed amplification of B. anthracis in phagocytes might be more important than the direct killing for photocatalysts to reduce the pathogenicity of the spores. These concepts might provide a new prospect to develop next generation antimicrobial agents.
Materials and Methods
Preparation of TiO2 substrates
Three types of films, TiO2, TiO2−xCx and TiO2−xNx, were prepared in an ion-assisted electron-beam evaporation system (Branchy Vacuum Technology Co., Ltd., Taoyuan, Taiwan). The distance between the rotating substrate holder and the electron-beam evaporation source was 550 mm. The chamber was evacuated with a mechanical pump (ALCATEL-2033SD, LACO Technologies, Salt Lake City, UT, USA) and a cryopump (Cryo-Torr8®, ULVAC Cryogenics, Chigasaki City, Kanagawa Prefecture, Japan) to a base pressure below 2.7×10−4 Pa. The substrates used were polished Si (100), quartz and glass coupons, which were sputter-etched with argon ions (Ar+) for 5 minutes prior to the deposition to remove any residual surface pollutants. The substrate temperature was maintained at 300°C with a quartz lamp. The TiO2 films were deposited in oxygen atmosphere (6.7 ×10−3 Pa) using rutile TiO2 (99.99%) as a source material. The nitrogen flow for TiO2−xNx films was 15 standard cm3 min−1 through the ion gun at a constant pumping speed and the chamber pressure was 4.4 ×10−2 Pa. The carbon dioxide gas flow for TiO2−xCx films was 7 standard cm3 min-1 and the chamber pressure was 2.6×10−2 Pa. The ion gun beam current of 10 mA and voltage of −1000 V was maintained by a Commonwealth Scientific IBS controller. Sufficient energy and current of the ion beam are critical to incorporate significant dopant concentration in the film. Without ion bombardment, it is difficult for the dopant to compete with the oxygen for incorporation into anatase titania. The deposition rate was adjusted to 0.2 nm·s−1 using a quartz crystal monitor for all films deposited at a thickness of 1.2 µm. The three types of films were prepared under the optimized conditions for their categories of anatase crystallinity and dopant concentration , . The structure and crystallinity of the films were investigated using a Rigaku D/MAX-2500V 18 kW low angle X-ray diffractometer (XRD) (Rigaku, Shibuya-Ku, Tokyo, Japan) operating with Cu-Kα radiation at 40 kV and 150 mA and a Renishaw 1000B Raman spectrometer equipped with a charge-coupled detector (CCD) and a CW 532 nm wave length diode pump solid state (DPSS) laser as the excitation source (Renishaw plc, Representative Office, Nantun District, Taichung, Taiwan). The UV-Vis absorption spectra were recorded on a Hitachi 3300H spectrophotometer (Hitachi Taiwan, Taipei, Taiwan).
Bacterial strains and culture
B. anthracis (ATCC 14186), which contains both pXO1 and pXO2 plasmids that express functional lethal toxin (LT) and edema toxin (ET), was grown and maintained as previously described , , . B. cereus (ATCC 13061) and B. thuringiensis (ATCC 35646) were maintained and cultured in nutrient agar or nutrient broth at 30°C , , and B. subtilis (ATCC 39090) was maintained and cultured in trypticase soy agar or broth at 37°C . All bacteria were stored in 50% medium and 50% glycerol solution in freezers at −80°C before use. To reactivate bacteria from frozen stocks, 25 µl bacterial stock solution was transferred to a test tube containing 5 ml of freshly prepared culture medium and then incubated at 30°C or 37°C under agitation overnight (16–18 hr). Spores of B. anthracis were prepared as previously described , . Overnight tryptic soy broth cultures of B. anthracis were diluted to about 107 CFU/ml in phosphate-buffered saline, and 0.1-ml aliquots were inoculated onto blood agar plates. The agar plates were incubated at 25–37°C until 90–99% phase-bright spores were observed by phase-contrast light microscopy (see below). Spores were harvested and washed with cold sterile distilled ionized (DI) water as previously described  and stored in DI water at 4°C until use for up to 2 weeks, changing the water at least once a week, or in the freezer at −20°C for up to a month. The quality of spores was determined by two complementary criteria previously established to validate the presence of dormant spores . The criteria consisted in the evaluation of (i) the absence of vegetative cells (rods) determined by microscopic examination as described, and (ii) the survival of spores in hydrochloric acid (2.5 N). Spore preparations of B. subtilis, B. cereus and B. thuringiensis were followed a similar protocol.
Photocatalytic reaction and detection of viable bacteria
In this study, bacterial concentrations were either determined by the standard plating method or inferred from optical density readings at 600 nm (OD600). For each Bacillus species, a factor for converting the OD600 values of the bacterial culture to concentration (CFU/ml) was calculated as follows. A fresh bacterial culture was diluted by factors of 10−1 to 10−7, and OD600 of these dilutions was measured. Bacterial concentrations of these dilutions were determined by the standard plating method. The OD600 values were plotted against the bacterial concentration log values, and the conversion factors for the particular bacteria were calculated from three independent measurements. For example, the conversion factor for B. subtilis was calculated to be 1×108 CFU/ml per OD600 by this method.
In order to determine the bactericidal effects of the TiO2-related substrates, 200 µl of bacterial overnight culture was transferred into 5 ml of culture medium and incubated at 37°C until an OD600 of 0.3 to 0.6 (log phase) was reached. The bacterial concentrations were calculated using the previously determined conversion factor for the bacteria, and the cultures were diluted to 1×105 CFU/ml with culture medium. One hundred microliters (1×104 CFU) was then applied to an area of approximately 1 cm2 of the different TiO2-related substrates using a plastic yellow tip. The bacteria substrates were then placed under an incandescent lamp (Classictone incandescent lamp, 60W, Philips, Taiwan) for photocatalytic reaction. A light meter (model LX-102, Lutron Electronic Enterprises, Taiwan) was used to record the illumination density. In the following photocatalysis experiments, the bacteria solution was supplied by 5–10 µl additional distil water every 5 minutes to maintain approximately 100 µl of total volume. After the photocatalyst-killing for 25 minutes, the bacteria containing solution approximately 85 µl was recovered from the photocatalyst substrates using a tip, additional 60 µl fresh medium was used to wash the remaining bacteria on the photocatalyst substrates. Two bacterial containing solutions were mixed, diluted and placed on agar plates. To test whether spores have different efficiency to adhere on TiO2 substrates that might influence the photocatalysis result, we analyze the spore recovery rates from TiO2, TiO2 (C) and TiO2, TiO2 (N) substrates. We found that the recovery rates are similar (data not shown), which has no statistic significant among these groups. In the dose-dependence experiments, illumination was carried out for 5 min at distances of 5, 10, and 15 cm from the lamp, corresponding to the illumination densities of 3×104, 1.2×103, and 3×102 lux (lumen/m2)(90, 30, and 10 mW/cm2), respectively. In the kinetic analysis experiments, illumination was carried out for 1, 5, 10, 15, and 25 min at a distance of 5 cm, corresponding to an illumination density of 3×104 lux (90 mW/cm2). Unless specified, illumination was carried out in a 4°C cold room to prevent over-heating of the photocatalyst substrates and prevent drying. After illumination, the bacterial solutions were recovered from the photocatalyst substrates, and an aliquot of fresh culture medium was used to collect the residual bacteria on the substrates. The two bacterial solutions were pooled to make a total volume of 150 µl. The bacterial concentration was determined by the standard plating method immediately after the bacterial collection, and the percentage of surviving bacteria was calculated. In spore experiments, 1×104 CFU (1×105 CFU/ml in 100 µl) were used, and the procedures followed the same protocols as in the live bacteria experiments.
Six to 8 week-old C57BL/6J mice were purchased from the National Experimental Animal Center (Taipei, Taiwan) , . The methods used in bacteremia experiments were modified from previous descriptions . Mortality of C57BL/6J mice from various anthrax spores treatments (from 1×106 to 1×107) was recorded within one week to serve as reference points. To determine the anti-bacterial effect of TiO2 (N), each mouse received an intravenous injection of 1×105 CFU spores of B. anthracis, a lethal dose for mice, with or without pretreatment by photocatalysis on TiO2 (N) or TiO2 substrates (3×104 lux, 10 minutes at 4°C). In the lethal toxin (LT) experiments, mortality of mice after a lethal dose of LT was performed based on previously described methods . Each mouse received an intravenous injection of LT (100 µg/g, LF:PA = 1∶5), a lethal dose for mice, with or without pretreatment of photocatalysis on TiO2 (N) or TiO2 substrates (3×104 lux, 10 minutes at 4°C or 25°C). The mortality of mice was then recorded. During the photocatalysis reaction, the distance between lamps with bacteria- or LT-containing photocatalyst substrates was 5 cm, corresponding to an illumination density of 3×104 lux (or 90 mW/cm2). Relative protein levels of PA and LF in the LT mixtures used in animal experiments were detected by Western blot using rabbit polyclonal anti-PA and anti-LF antibodies, and then probed by secondary horseradish peroxidase-conjugated goat anti-rabbit immunoglobulins , , . The gel intensities of PA and LF were measured using Image J software (version 1.32; National Institutes of Health, USA). The Animal Care and Use Committee of Tzu-Chi University approved the protocol of the mice experiments.
Cytotoxicity of LT was measured following a previously described method . In brief, a cytotoxic dose of LT (10 mg/L, LF:PA = 1∶5) with or without photocatalysis pretreatment on TiO2 and TiO2 (N) thin film was used to treat mouse macrophage J774A.1 cells. Three hours after the LT treatments, cell viability of J774A.1 cells were measured using a WST-1 kit (Roche, Mannheim, Germany), following the instructions provided by the manufacturer. Photocatalysis of purified LT was carried out as described in mouse experiments (3×104 lux, 10 min at 4°C).
Anthrax spores is normal saline (100 µl, 1×105 CFU/ml) were placed on cover glass, TiO2 and TiO2 (N) coated thin films , respectively. The spore-photocatalyst mixtures (100 µl) were then illuminated with visible light (Classictone incandescent lamp, 60W, Philips; 90 mW/cm2; lamp-target distance 10 cm) for 30 minutes. After illumination, the spore containing solutions (85 µl) were recovered from the photocatalyst substrates, and an aliquot of normal saline (60 µl) was used to collect the residual spores on the substrates. The two spore solutions were pooled to make a total volume of 145 µl. This spore solution was then added into one well of a six-well cell culture dish that containing confluent murine macrophage J774A.1 cells (1×106 cells/well) (MOI: 0.01 spores/cell). After phagocytosis was carried out for one, two and three hours, respectively, culture medium was removed, and 200 µl cell lysis buffer (100mM Tris-HCl [pH 7.4], 10mM MgCl2, 100mM NaCl, 0.2% sucrose, 0.5% Triton X-100) that was modified from previous literatures , , was then added to release the cell-engulfed or cell-bound spores. Additional 100 µl fresh medium was used to further collect the residual spores on the dishes. Two spore containing solutions were mixed and placed on agar plates. Cell culture medium (DMEM) without antibiotics and serum supplements was used in this analysis.
All results were calculated from data of at least three independent experiments. A t-test was used to assess the significance of differences in results of anti-microbial effects. A P value of less than 0.05 (P<0.05) was considered statistically significant. The statistical tests were carried out and output to graphs using Microsoft Excel (Microsoft Taiwan, Taipei, Taiwan) and SigmaPlot (Systat Software, Point Richmond, CA, USA) software.
Conceived and designed the experiments: JHK DSS HHH HHC. Performed the experiments: JHK HHH MSW. Analyzed the data: JHK MSW HHC. Contributed reagents/materials/analysis tools: JHK DSS MSW HCL HHC. Wrote the paper: HHC.
- 1. Dixon TC, Meselson M, Guillemin J, Hanna PC (1999) Anthrax. N Engl J Med 341: 815–826.
- 2. Christopher GW, Cieslak TJ, Pavlin JA, Eitzen EM Jr (1997) Biological warfare. A historical perspective. Jama 278: 412–417.
- 3. Hamburg MA (2002) Bioterrorism: responding to an emerging threat. Trends Biotechnol 20: 296–298.
- 4. Spotts Whitney EA, Beatty ME, Taylor TH Jr, Weyant R, Sobel J, et al. (2003) Inactivation of Bacillus anthracis spores. Emerg Infect Dis 9: 623–627.
- 5. Maness PC, Smolinski S, Blake DM, Huang Z, Wolfrum EJ, et al. (1999) Bactericidal activity of photocatalytic TiO(2) reaction: toward an understanding of its killing mechanism. Appl Environ Microbiol 65: 4094–4098.
- 6. Fujishima A, Honda K (1972) Electrochemical photolysis of water at a semiconductor electrode. Nature 238: 37–38.
- 7. Iwasaki M, Hara M, Kawada H, Tada H, Ito S (2000) Cobalt Ion-Doped TiO(2) Photocatalyst Response to Visible Light. J Colloid Interface Sci 224: 202–204.
- 8. Asahi R, Morikawa T, Ohwaki T, Aoki K, Taga Y (2001) Visible-light photocatalysis in nitrogen-doped titanium oxides. Science 293: 269–271.
- 9. Wong MS, Chu WC, Sun DS, Huang HS, Chen JH, et al. (2006) Visible-light-induced bactericidal activity of nitrogen-doped titania photocatalyst in eliminating the human pathogens. Appl Environ Microbiol 72: 6111–6116.
- 10. Weber MH, Marahiel MA (2002) Coping with the cold: the cold shock response in the Gram-positive soil bacterium Bacillus subtilis. Philos Trans R Soc Lond B Biol Sci 357: 895–907.
- 11. Nicholson WL, Munakata N, Horneck G, Melosh HJ, Setlow P (2000) Resistance of Bacillus endospores to extreme terrestrial and extraterrestrial environments. Microbiol Mol Biol Rev 64: 548–572.
- 12. Schnepf E, Crickmore N, Van Rie J, Lereclus D, Baum J, et al. (1998) Bacillus thuringiensis and its pesticidal crystal proteins. Microbiol Mol Biol Rev 62: 775–806.
- 13. Drobniewski FA (1993) Bacillus cereus and related species. Clin Microbiol Rev 6: 324–338.
- 14. Wang H, Lewis JP (2006) Second-generation photocatalytic materials: anion-doped TiO2. J Phys Condens Matter 18: 421.
- 15. Collier RJ, Young JA (2003) Anthrax toxin. Annu Rev Cell Dev Biol 19: 45–70.
- 16. Chang HH, Tsai MF, Chung CP, Chen PK, Hu HI, et al. (2006) Single-step purification of recombinant anthrax lethal factor from periplasm of Escherichia coli. J Biotechnol 277–285.
- 17. Dixon TC, Fadl AA, Koehler TM, Swanson JA, Hanna PC (2000) Early Bacillus anthracis-macrophage interactions: intracellular survival survival and escape. Cell Microbiol 2: 453–463.
- 18. Ireland JC, Klostermann P, Rice EW, Clark RM (1993) Inactivation of Escherichia coli by titanium dioxide photocatalytic oxidation. Appl Environ Microbiol 59: 1668–1670.
- 19. Bekbolet M, Araz CV (1996) Inactivation of Escherichia coli by photocatalytic oxidation. Chemosphere 32: 959–965.
- 20. Yu JC, Ho W, Yu J, Yip H, Wong PK, et al. (2005) Efficient visible-light-induced photocatalytic disinfection on sulfur-doped nanocrystalline titania. Environ Sci Technol 39: 1175–1179.
- 21. Hu C, Lan Y, Qu J, Hu X, Wang A (2006) Ag/AgBr/TiO2 visible light photocatalyst for destruction of azodyes and bacteria. J Phys Chem B 110: 4066–4072.
- 22. Shieh KJ, Li M, Lee YH, Sheu SD, Liu YT, et al. (2006) Antibacterial performance of photocatalyst thin film fabricated by defection effect in visible light. Nanomedicine 2: 121–126.
- 23. Elahifard MR, Rahimnejad S, Haghighi S, Gholami MR (2007) Apatite-coated Ag/AgBr/TiO(2) visible-light photocatalyst for destruction of bacteria. J Am Chem Soc 129: 9552–9553.
- 24. Li Q, Xie R, Li YW, Mintz EA, Shang JK (2007) Enhanced visible-light-induced photocatalytic disinfection of E. coli by carbon-sensitized nitrogen-doped titanium oxide. Environ Sci Technol 41: 5050–5056.
- 25. Cheng CL, Sun DS, Chu WC, Tseng YH, Ho HC, et al. (2009) The effects of the bacterial interaction with visible-light responsive titania photocatalyst on the bactericidal performance. J Biomed Sci 16: In Press.
- 26. Russell AD (1990) Bacterial spores and chemical sporicidal agents. Clin Microbiol Rev 3: 99–119.
- 27. Driks A (1999) Bacillus subtilis spore coat. Microbiol Mol Biol Rev 63: 1–20.
- 28. Fouet A, Mock M (2006) Regulatory networks for virulence and persistence of Bacillus anthracis. Curr Opin Microbiol 9: 160–166.
- 29. Zan L, Fa W, Peng T, Gong ZK (2007) Photocatalysis effect of nanometer TiO2 and TiO2-coated ceramic plate on Hepatitis B virus. J Photochem Photobiol B 86: 165–169.
- 30. Guidi-Rontani C, Levy M, Ohayon H, Mock M (2001) Fate of germinated Bacillus anthracis spores in primary murine macrophages. Mol Microbiol 42: 931–938.
- 31. Guidi-Rontani C, Weber-Levy M, Labruyere E, Mock M (1999) Germination of Bacillus anthracis spores within alveolar macrophages. Mol Microbiol 31: 9–17.
- 32. Cote CK, Rossi CA, Kang AS, Morrow PR, Lee JS, et al. (2005) The detection of protective antigen (PA) associated with spores of Bacillus anthracis and the effects of anti-PA antibodies on spore germination and macrophage interactions. Microb Pathog 38: 209–225.
- 33. Kudva IT, Griffin RW, Garren JM, Calderwood SB, John M (2005) Identification of a protein subset of the anthrax spore immunome in humans immunized with the anthrax vaccine adsorbed preparation. Infect Immun 73: 5685–5696.
- 34. Yang MC, Yang TS, Wong MS (2004) Nitrogen-doped titanium oxide films as visible light photocatalyst by vapor deposition. Thin Solid Films 1–5.
- 35. Yang TS, shiu CB, Wong MS (2004) Structure and hydrophilicity of titanium oxide films prepared by electron beam evaporation. Surface Science 548: 75–82.
- 36. Kau JH, Lin CG, Huang HH, Hsu HL, Chen KC, et al. (2002) Calyculin A sensitive protein phosphatase is required for Bacillus anthracis lethal toxin induced cytotoxicity. Curr Microbiol 44: 106–111.
- 37. Kau JH, Sun DS, Tsai WJ, Shyu HF, Huang HH, et al. (2005) Antiplatelet Activities of Anthrax Lethal Toxin Are Associated with Suppressed p42/44 and p38 Mitogen-Activated Protein Kinase Pathways in the Platelets. J Infect Dis 192: 1465–1474.
- 38. Bizani D, Brandelli A (2004) Influence of media and temperature on bacteriocin production by Bacillus cereus 8A during batch cultivation. Appl Microbiol Biotechnol 65: 158–162.
- 39. Li E, Yousten AA (1975) Metalloprotease from Bacillus thuringiensis. Appl Microbiol 30: 354–361.
- 40. Kort R, O'Brien AC, van Stokkum IH, Oomes SJ, Crielaard W, et al. (2005) Assessment of heat resistance of bacterial spores from food product isolates by fluorescence monitoring of dipicolinic acid release. Appl Environ Microbiol 71: 3556–3564.
- 41. Carrera M, Zandomeni RO, Fitzgibbon J, Sagripanti JL (2007) Difference between the spore sizes of Bacillus anthracis and other Bacillus species. J Appl Microbiol 102: 303–312.
- 42. Sagripanti JL, Bonifacino A (1996) Comparative sporicidal effects of liquid chemical agents. Appl Environ Microbiol 62: 545–551.
- 43. Sun DS, King CC, Huang HS, Shih YL, Lee CC, et al. (2007) Antiplatelet autoantibodies elicited by dengue virus non-structural protein 1 cause thrombocytopenia and mortality in mice. J Thromb Haemost 5: 2291–2299.
- 44. Chang JC, Chang HH, Lin CT, Lo SJ (2005) The integrin alpha6beta1 modulation of PI3K and Cdc42 activities induces dynamic filopodium formation in human platelets. J Biomed Sci 12: 881–898.
- 45. Sun DS, Lo SJ, Lin CH, Yu MS, Huang CY, et al. (2005) Calcium oscillation and phosphatidylinositol 3-kinase positively regulate integrin alpha(IIb)beta3-mediated outside-in signaling. J Biomed Sci 12: 321–333.
- 46. Chang HH, Shih KN, Lo SJ (2000) Receptor-mediated endocytosis as a selection force to enrich bacteria expressing rhodostomin on their surface. J Biomed Sci 7: 42–50.
- 47. Leahy MB, Dessens JT, Nuttall PA (1997) Striking conformational similarities between the transcription promoters of Thogoto and influenza A viruses: evidence for intrastrand base pairing in the 5′ promoter arm. J Virol 71: 8352–8356.