The present in vitro study served as a proof-of-principle investigation for evaluating whether bacterial acid challenge can cause release of Ca2+ ions and consequent pH-buffering effects from the potentially caries-protective oral care agent HAP when it is present at relatively high concentrations in planktonic cultures and biofilms. For this purpose, planktonic cultures and biofilms of S. mutans served as model systems. S. mutans is well known for its role in the pathogenesis of dental caries and its ability to extensively produce extracellular polymeric substances that promote bacterial attachment and biofilm formation [23]. For this study, S. mutans was chosen rather than other caries-associated bacteria due to its pronounced acidogenic [24] and aciduric [25] properties.
In the first part of this study, planktonic cultures of S. mutans were grown either in pure nutrient broth or nutrient broth with 5% HAP or with 5% silica. The relatively high concentration of 5% was chosen analogously to a recent in situ study, which used a 5% HAP mouthwash and showed some slightly anti-adhesive effects of this mouthwash [18]. Silica is a frequently used toothpaste abrasive [26], and was included as control for excluding potential impairing effects of particles on bacterial growth or biofilm formation. Due to the experimental set-up (i.e. culture on an orbital shaker for keeping HAP or silica particles dispersed), it was inevitable to culture S. mutans under aerobic conditions. Ahn et al. described several biochemical and phenotypic changes in S. mutans during aerobic growth (including acidogenicity), but also concluded that S. mutans is highly adaptable to different environments [27]. On the contrary, Higuchi et al. showed that the growth of the S. mutans strain used in the present study (DSM 20523, NCTC 10449) was enhanced by oxygen and retarded by anaerobiosis. Furthermore, this specific strain also produced more lactate under aerobic conditions, whereas anaerobiosis led to heterolactic fermentation with production of mainly ethanol and formate [28]. Accordingly, pH values around pH 4.5 after 48 h clearly showed relevant acid production from S. mutans although these cultures may have mainly comprised bacterial cells in a stationary phase due to the rather high starting inoculum. Sucrose (at a concentration of 1%) was chosen as a carbon source in the nutrient broth because this has been found to be support the highest acid production from S. mutans [29, 30].
In the presence of HAP, there was a significant release of Ca2+ resulting in median Ca2+ concentrations in the nutrient broth of 38.9 or 38.1 μg/mL after 24 or 48 h respectively. Salivary Ca2+ concentrations have been reported to range between 20 and 55 μg/mL [11, 31,32,33]. This means that, under the given experimental conditions, Ca2+ release from HAP was in the same range as the concentration of human salivary Ca2+ and may thus be considered relevant, although HAP dispersed in planktonic bacteria does not directly resemble any natural situation in the oral cavity. On the other hand, the slight but significant Ca2+ increases found for the silica group as compared to the group with nutrient broth alone may be attributed to minor calcium impurities in the chosen silica. After 24 h and 48 h of planktonic culture, there was a tendency for slightly higher pH in the HAP group as compared to the other two groups.
These results could be affirmed in the biofilm experiments which may be more relevant with respect to the natural situation in vivo. Here, S. mutans biofilms were incubated for 72 h in total, whereby after 24 h either pure nutrient broth or nutrient broth with 0.5% HAP or with 0.5% silica were allowed to sediment on the preformed initial biofilms and after 48 h nutrient broth with 1% sucrose was added to promote bacterial acid production. The use of single-species S. mutans biofilms may be seen as a limitation here but polymicrobial biofilms may have caused problems in terms of species-species interactions that may have diminished acid production. Therefore, we chose a single-species biofilm model with an S. mutans strain that is known to produce high loads of lactic acid [28]. The concentration of 0.5% of HAP or silica, respectively, was chosen to mimic dilution effects as they may occur in the oral cavity after using a mouthwash with 5% HAP [18]. In contrast to previous works [34, 35], we used no filter-sterilized saliva here to promote biofilm formation as salivary Ca2+ ions (concentrations between 20 and 55 μg/mL [11, 31,32,33], as described above), may have impeded Ca2+ release measurements.
After 72 h of biofilm culture, there was a clear Ca2+ release corresponding to median Ca2+ concentrations of 43.4 or 56.5 μg/mL in the supernatants and suspended biofilms, respectively, while no such effects were found in either of the other groups. Therefore, HAP may act as a calcium reservoir when present in dental biofilms and release Ca2+ following bacterially induced pH drops, thus potentially reducing demineralization by providing supersaturation with respect to calcium phosphate in the plaque fluid. Zhang et al. investigated whether the presence of biofilms has effects on the treatment outcomes of nano-HAP and sodium fluoride [36]. They cultured biofilms on artificially demineralized enamel specimens and subjected them to a pH-cycling schedule with twice daily applications of nano-HAP or sodium fluoride. For nano-HAP treatment, they found an enhanced demineralization protection in specimens with biofilms during pH-cycling which they attributed to the high calcium content in the biofilms that may act as a diffusion barrier, potentially slowing the outflux of calcium and phosphate [36]. Accordingly, Shaw et al. found as early as 1983 that Ca2+ concentrations in plaque were statistically significantly higher in caries-free children (anterior plaque: 11.55 μg/mg dry weight; posterior plaque: 3.57 μg/mg) compared to children who had been highly caries-active within the last two years, exhibiting a mean DMFS of 25.9 (anterior plaque: 2.57 μg/mg; posterior plaque: 1.63 μg/mg) [31].
Interestingly, pH was found to be significantly higher (about 0.5 pH units) in suspended biofilms of the HAP group compared to the other two groups. The buffering effects observed for HAP may be explained by its chemical properties. Calcium phosphates in general are basic and release Ca2+ and (hydrogen)phosphate ions H2PO4− and HPO42− under acidic conditions. The corresponding equation for HAP around pH 4.5 (like in the present study) is, as follows:
$$ {\mathrm{Ca}}_5{\left({\mathrm{PO}}_4\right)}_3\left(\mathrm{OH}\right)+7\ {\mathrm{H}}^{+}\rightarrow 5\ {\mathrm{Ca}}^{2+}+{\mathrm{H}}_2\mathrm{O}+3\ {\mathrm{H}}_2{{\mathrm{PO}}_4}^{-} $$
The release of H2PO4− may act as an additional buffer system similar to the phosphate buffer system found in human saliva [5, 12]. An in vitro study showed that the buffering range of calcium phosphates is around pH 4 [37]. Thus, HAP may show its best buffering efficacy in highly acidic environments like cariogenic biofilms following carbohydrate ingestion as in the present study. Nedeljkovic et al. evaluated the buffering ability of dental restorative materials and included HAP discs as a control material [38]. They found the highest buffering capacity among the tested materials for HAP and observed higher pH increases for lower starting pH values, which they attributed to increasing dissolution of HAP with decreasing pH [38].
These findings are in accordance with Huang et al. who investigated the remineralizing effects of nano-HAP on demineralized bovine enamel under pH-cycling conditions [19]. They found that the surface microhardness increased and the integrated mineral loss significantly decreased as pH decreased, with the most effective group found at pH 4 [19]. In contrast, Zhang et al. found no increased remineralization in their study described above. They explained the discrepancy to the findings from Huang et al. by different components in their remineralization/demineralization buffers (mainly proteins) which may block the enamel surface to some extent [36]. In a recent in situ-study, Amaechi et al. found remineralization of artificially produced carious lesions on enamel blocks that were worn in situ on intra-oral appliances after use of a toothpaste containing 10% HAP [39].
Lately, it was also reported that application of CPP-ACP may have prebiotic-like effects on microbial ecology in highly cariogenic environments by increasing the buffering capacity of the biofilm and favoring growth of commensal species [40, 41]. Given the findings reported here, this may also hold true for other calcium phosphates like HAP.
Although these findings are promising, there are two limitations of this study that must be considered when interpreting its results: 1) HAP was sedimented onto the biofilms after 24 h of culture. So, it is not clear whether HAP accumulates in oral biofilms in vivo, although Vogel et al. already demonstrated the general possibility for accumulation of calcium phosphates in dental plaque when evaluating Ca2+ concentrations in plaque fluid after use of an α-TCP-containing chewing gum [11]. 2) HAP was added to the biofilms in a relatively high concentration (0.5%) that may exceed the concentrations found in dental biofilms in vivo. For these reasons, the present study only resembles “optimal conditions”. Future studies will have to show whether and to what extent synthetic HAP accumulates in oral biofilms following application of HAP-containing oral care products like mouthwashes. Furthermore, comparing Ca2+ release from different calcium phosphates like HAP, ACP or α−/β-TCP upon bacterial acid challenge may be an interesting topic for further studies.