CYTOTOXICITY OF METAL IONS RELEASED BY AN ALUMINIUM BRONZE DENTAL MATERIAL. SYNERGIC EFFECT OF THE MIXTURE OF IONS. Claudia Grillo1, María L. Morales2, María V. Mirífico 1,2*, Mónica Fernández Lorenzo de Mele 1,2* 1 Instituto de Investigaciones Fisicoquímicas Teóricas y Aplicadas (INIFTA, CCT La Plata-CONICET), Facultad de Ciencias Exactas, Departamento de Química, Universidad Nacional de La Plata, Casilla de Correo 16, Sucursal 4, 1900 La Plata, Argentina 2 Facultad de Ingeniería, Áreas Departamentales Ingeniería Química y Mecánica, Universidad Nacional de La Plata, Calle 47 y 1, 1900 La Plata, Argentina E-mail: mirifi@inifta.unlp.edu.ar - mmele@inifta.unlp.edu.ar Abstract. Aluminium bronzes have appeared as economical substitutes of conventional gold rich alloys to fabricate crowns and bridges. However, a very low corrosion resistance and possible cytotoxic effects on surrounding cells were reported. The aim of this work is to study the dissolution of an aluminium bronze and the cytotoxic effects of the ions released on osteoblastic cell line. Conventional electrochemical techniques and atomic absorption spectroscopy to obtain the average concentration (AC) of ions were employed to study the corrosion process. The cytotoxicity was evaluated by a) ions released by the metal alloy immersed in the cell culture and b) salts of the metal ions. Results showed that the AC of the metal ions released can not be predicted on the basis of the overall composition of the alloy. Cytotoxic effects in cells of the vicinity of the metal were observed. Importantly, synergistic effects were found when Al-Zn ion combinations and mixtures of the ions at 9 x AC concentrations were employed. These results were interpreted considering the synergistic effects and a diffusion controlled mechanism that, in the metal surroundings, yields to concentration levels several times higher than the AC value. Keywords: Cytotoxicity, Metal ion, Dental alloy, Metallic salt 1. INTRODUCTION Despite expressed doubts as to their suitability (Stoffers et al, 1987) copper base alloys have been used as dental casting alloys for fixed prosthesis in the U.S., Japan, South America and some countries of Eastern Europe for more than 25 years. (Tibballs and Erimescu, 2006; Eschler et al, 2003) According to dental technicians and dental suppliers their popularity is due to their good mechanical strength, high elastic modulus, low density, its bright yellow color with strong resemblance gold and its low cost relative to noble metal alloys. (Ardlin et al, 2009) Clinical studies have shown that corrosion of crowns and posts of such alloys causes staining and inflammatory processes in the surrounding gum tissue and blue-green pigment in the roots of teeth. (Arvidson et al, 1980; McGuiness et al, 1987) Furthermore, high levels of toxic elements were found after static immersion testing in cell cultures (Ardlin et al, 2009). Thus, the widespread use of copper based alloys is a cause of great concern due to the undesirable effects found on surrounding cells by metals ions released from these alloys (Cu, Ni, Zn, Al). (Tibballs and Erimescu, 2006; Ardlin et al, 2009; Arvidson et al, 1980; Arvidson and Wróblewski, 1978). Biocompatibility of dental alloys is strongly related to their metal ions release. (Elshahawy et al, 2009). The biological effects of these metal ions are significantly different and depend of several factors such as oral environment, exposure time, nature and amount of release metal cations (not generally proportional to the abundance of each metal in the alloy), etc. (Schmalz et al, 1998) Different sources of ions have been employed in cytotoxic studies: a) the extracts obtained from the dissolution of a metallic sample ex situ and then added to the cell culture (extract contact: ExtC) (Wataha et al, 2001; Granchi et al, 1998; Bumgardner et al, 2002); b) the dissolution of metal samples in situ (direct contact: DC) (Wataha et al, 1992; Bumgardner and Lucas, 1995; Grill et al, 2000; Grill et al, 1997; Kapanen et al, 2002; Kapanen et al, 2001); c) the metal salts added to the cell culture (ES). (Huk et al, 2004; Fleury et al, 2006; Craig and Hanks, 1990; Merrit et al, 1984; Schmalz et al, 1998; Wataha et al, 2000; Wataha et al, 2002). One of the copper based alloys widely employed is an aluminium-bronze commercially available as Ventura Orcast PLUS®. It is featured to be used for fixed dental prosthesis like crowns and bridges covered with resins but it is also employed in endodontical posts. The aim of this work is to study the cytotoxic effects of the ions released by the Orcast PLUS® casting alloy as a response to the increasing demand of control of dental materials. The highly toxic environment provoked by the release of ions is also a suitable area of study to assess an additional purpose: to elucidate the cause of the different behaviour of cells in relation to a) ions released by a metal alloy immersed in the cell culture (in situ) and b) the presence of equivalent amounts of salts of the metal ions added to the cell culture. For this reason, the effect of a disc of the copper based dental casting alloy on the surrounding cells and the variation of the cytotoxic effect with distance between cells and the source of ions were assessed in this work. Conventional electrochemical techniques were employed to study the corrosion process and the concentration of the ions released was measured by atomic absorption spectroscopy. The cytotoxic effect on osteoblastic cells of individual ions, some combinations of two ions and the mixtures of all the ions of the alloy components were also analyzed to investigate possible synergic effects. 2. MATERIALS AND METHODS 2.1. Cells culture Rat osteosarcoma derived cells (UMR 106 line) was originally obtained from American Type Culture Collection (ATCC) (Rockville, MD, USA). Cells were grown as monolayer in Falcon T-25 flasks with 10 ml D-MEM culture medium (GIBCO-BRL, Los Angeles, USA) supplemented with 10% inactivated fetal calf serum (Natocor, Carlos Paz, Córdoba, Argentina), 50 IU/ml penicillin and 50μg/ml streptomycin sulfate (complete culture medium) at 37º C in a 5% CO2 humid atmosphere. Cells were counted in an improved Neubauer haemocytometer and viability was determined by the exclusion Trypan Blue (Sigma, St. Louis, MO, USA) method; in all cases viability was higher than 95%. 2.2. Copper based alloy and metal ions released The copper based alloy (CuBA) used in the assays was Orcast PLUS ® (Cu 81.5%, Al 7%, Ní 4.5%, Fe 3%, Mn 2% and Zn 2%) (Madespa S.A., Toledo, Spain). Cylindrical casting copper and CuBA electrodes, casting CuBA discs for experiments with cells and casting CuBA samples for atomic absorption spectroscopy were made by lost wax casting process (Macchi, 2000). With this objective a wax pattern with the suitable shapes for each purpose was formed. To assess the metal ions release square shape sheets of the casting copper alloy of ca. 49 cm2 of geometrical area were immersed in synthetic saliva (SS: NaCl 0.40 gr/l, KCl 0.40 gr/l, CaCl2 0.80 gr/l, NaH2PO4 0.16 g/l, urea 1.00 g/l, KSCN 0.16 g/l; pH = 4.77) (200 mL) for 24 h, at 37o C. After this period, the metal ions concentration was measured by flame atomic absorption spectrophotometry. Each measurement was repeated three times in independent experiments. 2.3. Corrosion tests The electrochemical experiments were performed in a conventional undivided gastight glass cell with dry nitrogen gas inlet and outlet. The working electrode was an Orcast PLUS® bar encapsulated in Teflon, with an exposed geometrical circular area of 0.1256 cm2, the counter-electrode was a 2 cm2 Pt foil and as reference a saturated calomel electrode (sce) (to which all potentials reported are referred) was used. A computer controlled PAR 273A potentiostat was employed for experiments. The potentiodynamic measures were performed in nitrogen deareated SS (20 mL) and in nitrogen deareated culture medium (D-MEM, pH=7) (20 mL). Prior to each electrochemical measurement, the working electrodes were prepared according to previous reports (Grillo et al, 2009). Potentiodynamic polarization curves of CuBA and copper electrodes exposed to the synthetic saliva were obtained in the conventional way. Potentiodynamic scans were made at 5 mVs-1 sweep rate (v) and started at -0.580 V in the anodic direction to +0.050 V. Prior to each measurement the electrode was subjected to a cathodic pre-treatment by holding it potentiostatically at -0.580 V for 60 s, to reduce oxide film possibly formed in air. Each potentiodynamic experiment was repeated at least three times to check the reproducibility and the polarization curves were repetitive. 2.4 Metal ion solutions for cytotoxicity assays Cytotoxicity tests caused by the metal ions were made using the corresponding salts dissolved in the culture medium. The concentration of the salts corresponds to the average concentration level reached after 8h of immersion in saliva (AC8h), measured by atomic absorption spectroscopy. This AC8h value was calculated based on the atomic absorption spectroscopy analysis and assuming that a sample of 3 cm2 of geometric area was exposed to 1 mL of synthetic saliva during 8 h (sleeping period). Concentrations corresponding to 15, 30 and 60 times higher than this minimum level were also assayed. The evaluation of cytotoxicity of metal ions was made by exposures to solutions of different concentrations of the corresponding metal salts obtained from Merck Chemical Co. (Darmstadt, Germany). The metal salts included, copper (CuCl2.6 H2O), aluminum (AlCl3), nickel (NiCl2.6H2O), iron (FeCl2. 6 H2O) manganese (MnCl2.4H2O) and zinc (ZnCl2) salts. 2.5 Evaluation of the effect of metal ions released from the aluminium bronze by Acridine Orange staining For this set of experiments 4.5 x 104 cells were seeded in Petri dish (100 mm diameter) and grown at 37ºC in 5% CO2 humid atmosphere in complete culture medium (D-MEM, pH=7), for 24 h. Then, the medium was removed, a 4 mm diameter CuBA alloy disc was added in the center of each Petri dish, and immediately fresh medium was incorporated. Cells were grown under these conditions during different periods: 3, 24 and 48 h. UMR 106 cell culture without the alloy disc were used as negative controls. To facilitate the analysis of cytotoxic effects as a function of the distance from the source of ions, the area with cells was divided in regions A1, A2, B and C according to Fig. 1. After exposure periods, adherent cells were stained with Acridine Orange dye (Sigma, St Louis, MO, USA) and immediately after, they were examined by fluorescence microscopy (Olympus BX51, Olympus Corp., Tokyo, Japan) equipped with appropriated filter, connected to an Olympus DP71 (Olympus Corp., Tokyo, Japan) color video camera. The images were taken immediately after opening the microscope shutter to the computer monitor. Fig. 1. Scheme of the regions of the Petri dish and the disc of Orcast PLUS® copper based alloy in the center. The radii (r) of the regions are: rA1 = 0.9 cm; rA2 = 1.4 cm; rB = 2.4 cm; rC = 3.4 cm. 2.6. Evaluation of the colony formation (CF) Colony formation or clonogenic assay is an in vitro cell survival assay based on the ability of a single cell to grow into a colony (Franken et al, 2006). For this analysis 50 cells/Petri dish were grown at 37° C in 5% CO2 humid atmosphere in complete culture medium in presence of an alloy disc in the center of each place. An additional cell culture without alloy disc was used as negative control. After incubation for 7 days the colonies of acceptable size were taken into account for scoring. They were fixed with methanol: acetic acid (3:1) and stained with Acridine orange. The enumeration and classification of colonies (cell clusters), was made under fluorescence microscopy with a 40x objective (Olympus BX51, Olympus Corp., Tokyo, Japan). Two experiments were performed in independent trials to assess reproducibility. 2.7. Determination of cytotoxicity of metal ions by Neutral Red assay Metals ions cytotoxicity was estimated in UMR-106 cells by Neutral Red (NR) assay (Borenfreud and Puerner, 1984). This assay measures cellular transport based on the dye uptake by living cells. Absorbance change is directly proportional to the number of viable cells. For this analysis 2.7 x 103 cells/well were cultured in 96 multi-well plate in complete culture medium for 4 h. Then, the cell were grown in presence of the different metal ions concentrations during 24 h. The NR uptake assay was performed according to previous reports (Grillo et al, 2009). Ethanol (7%) was used as positive control. Cytotoxicity percentage was calculated as [(A–B) /A] × 100, where A and B are the absorbance of control and treated cells, respectively. Each experiment was repeated in two independent assays every one including 16 wells, that is 32 wells for each concentration tested. Data were analyzed using one-way ANOVA test and multiple comparisons were made using p values corrected using the Bonferroni method. 3. RESULTS 3.1. Corrosion test Potentiodynamic polarization curves for CuBA immersed in synthetic saliva solution (SS, pH = 4.77) and in cell culture medium (CCM, pH = 7.0) (Fig. 2a) showed similar electrochemical response immediately after the immersion, in the potential zone that includes the open circuit potentials (-0.250 V) and up to ca. -0.050 V. Fig. 2a. Typical potentiodynamic polarization curves for Orcast PLUS® copper based alloy immediately after immersion in deaerated (——) synthetic saliva solution (SS, pH = 4.77) and (— •) culture medium (CCM, pH = 7.0), at 37° C. Potentiodynamic polarization curve for copper, the metal base of alloy, is included for comparison: (- - -): SS, pH = 4.77, (• • •): CCM, pH = 7.0. When the electrode had previously been immersed in SS (Fig. 2b) and CCM (Fig. 2c), and then the polarization curves were recorded, corrosion current markedly diminished in both media indicating that the dissolution process decreases with time, after an initial strong electrodissolution process. Fig. 2b. Typical potentiodynamic polarization curves for Orcast PLUS® copper based alloy measured (——) immediately, after (- - -) 30 min, and (•••) 60 and 1080 min of immersion in deareated and quiet artificial saliva, at 37° C. Fig. 2c. Typical potentiodynamic polarization curves for Orcast PLUS ® copper based alloy measured (——) immediately, after (— —) 60 min, (- - - -) 180 min, and (•••••••) 1440 min of immersion in deaerated and quiet culture medium, at 37° C. With the aim of comparison, polarization curves measured with pure copper were also included in Fig. 2a. In this case current intensity values corresponding to SS (pH = 4.77) are lower than those of CCM (pH = 7.0) revealing a marked effect of pH and organic substances present in CCM on copper dissolution. In the case of CuBA the electrochemical response is more complex and the influence of the medium composition is not so evident. 3.2. Effects metal ions released by CuBA on the number of living cells as a function of the distance from the metal The influence of the distance from the source of metal ions on cell viability was measured by epifluorescence microscopy after Acridine Orange staining. These assays showed (gray bars, Fig. 3) that after 3 h exposure those cells which were close to the metal surface (Region A1) were severely altered (p < 0.001). For longer distances (regions A2, B, C) a slight decrease in the number of living cells to 85% of the control value was detected indicating that they were less affected by the metal ions released by the copper alloy. Fig. 3. Viability of cells by of the Acridine Orange staining after 3, 24 and 48 h exposure to CuBA. Variation with the distance from CuBA disc. Regions A1, A2, B and C according to Fig. 1. 3.3. Effect of metal ions released by CuBA on the number living cells as a function of exposure time The effect of possible high local concentration of ions in the vicinity of the metallic alloy was also investigated after exposures to the metal for complete growth periods. In this case both, cell duplication and the accumulation of ions released by the biomaterial occur simultaneously. After 24 h and 48 h, epifluorescence microscopy images revealed that the deleterious effect on the growing cells is again more notorious in region A1 (Fig. 3) where strong reductions to 30 and 5% in the number of cells related to the control value were detected, respectively. Interestingly, higher number of cells than in the case of 3 h assay was found in the zones A2, B, C after 24 h (24 h data, Fig. 3), indicating that cells were able to duplicate during this period. Conversely, new young cells were severely altered by the metal ions during the following growth period (48 h data, Fig. 3). This resulted in a marked decrease (close to 60% of the control value) of the number of cells after a 48 h period in regions A2, B, C. 3.4. Effect of metal ions released by CuBA on colony forming units Colony forming units assays showed that, in the vicinity of the alloy (region A1), after 7 days of exposure to the metal ions released from the alloy disc, a drastic decrease in the number of colonies was observed with respect to the control experiment without the metal (Table 1). Additionally, microscopic observations revealed that the average diameters of the colonies corresponding to the control and those grown with CuBA were 112.21 ± 5.45 μm and 80.83 ± 4.95 μm. This result indicates an important effect of the ions released by CuBA on the size and number of the colonies. In Table 1 colonies with diameters in the 95 μm to 150 μm were considered as large colonies while those with shorter diameters as small colonies. Type of colony Small colonies Large colonies Total % Disc surroundings (A1 region) 10.46 (0.40) 6.23 (0.71) 16.69 (1.11) % Out of A1region* 59.56 (1.21) 23.75 (0.81) 83.31 (2.02) * Standard Errors are between brackets Table 1. Enumeration of colonies within region A1 and out of A1 according to their sizes after 7 days of exposure to the metal disc. 3.5. Measurements of the amount of ions released from the metal surface Results presented in Fig. 3 and Table 1 show a notorious temporal and spatial dependent effect of the mixture of metal ions released by the copper alloy on the cell growth. The different components of the alloy (Cu, Al, Ni, Fe, Mn, Zn) may be involved in this deleterious action. In order to quantify the metal ions released by the copper alloy, atomic absorption measurements were performed (Table 2). Interestingly, the release of a particular element showed in Table 2 is not related with its atomic percent in the alloy. Thus, the % of copper and aluminium in the alloy are 81.5%, and 7%, respectively, however a lower level of copper ions than aluminium ions (0.175 and 9.797 μg/cm2, respectively) was detected in the synthetic saliva where the CuBA was immersed during 24 h (Table 2). Metal ion Copper Aluminium Nickel Iron Manganese Zinc Concentration of the metal ion released by CuBA in synthetic salivaa mg/L µg/cm2 0.041 ± 0.014 0.175 ± 0.068 2.384 ± 1.958 9.797 ± 7.923 0.088 ± 0.015 0.376 ± 0.078 0.113 ± 0.076 0.493 ± 0.341 0.071 ± 0.015 0.306 ± 0.078 0.102 ± 0.022 0.439 ± 0.112 Composition of CuBA (%w/w) 81.5 7.0 4.5 3.0 2.0 2.0 a Detection limits (mg/L): Cu=0.005; Al=0.024; Ni=0.006; Fe=0.006; Mn=0.008; Zn=0.007 Table 2. Concentration of the metal ions released by CuBA in synthetic saliva, after 24 h of immersion at 37° C. 3.6. Cytotoxicity of metal ions by Neutral Red assays: Effect of the ions from metal salts Lysosomal activity (Neutral Red assay) in UMR-106 cell line after treatments with the ions of each of the alloy components was assayed. For these experiments the minimum concentration tested (AC8h) for each ion was proportional to the average concentration measured by atomic absorption spectrophotometry, referred to a 3 cm2 dental alloy (as a source of metal ions release) that was exposed to 1 mL of saliva during 8 h (sleeping period). Assays with AC8h concentration with single ions did not show any decrease in the lysosomal activity. Similarly, the mixture with all the metal ions did not show any effect. It could be inferred that AC8h of both, individual ions or the total mixture, is below the cytotoxic threshold value and consequently does not affect the cellular activity. However, these results are in disagree with the reduction in the number of living cells that were observed in region A1, close to the metal, shown in Fig. 3. Probably the concentration of ions in the region A1 may be several times higher than that of the bulk. In addition, experiments using metal ions levels several times higher than AC8h were performed. The results show that no significant effects were found for single Mn, Fe, Ni, Cu and Zn ions, when the concentrations employed were 30 times higher than the average (30 x AC8h). In the case of Al, the solubility limit impeded the use of concentrations higher than 9x AC8h Experiments with higher concentrations (60 x AC8h) only showed weak deleterious action for Mn and strong for Zn (p < 0.001) (Fig. 4). A slight increase in lysosomal activity was found in the case of Fe. 140 120 % Control 100 80 60 40 20 0 Control Mn Fe Ni Cu Zn Control + Metal Ions Fig. 4. Cytotoxicity of metal ions at 60 fold minimum concentration tested (60 x AC8h) by Neutral Red assay. In case of Zn ions, Fig. 5 shows that when different concentrations between 9 x AC8h and 60 x AC8h were assayed only concentrations ≥ 36 x AC8h markedly affect the lysosomal activity of cells. Fig. 5. Effect of Zn ions on the lysosomal activity of cells at concentrations in the 9 x to 60 x AC8h. In the case of Al ions a slight reduction in lysosomal activity, ca. 80 - 90 % of the control, in Al 4.5 - 7.5 x AC8h concentration range was detected but a reduction to ca. 40% was observed for 9 x AC8h (Fig. 6). Fig. 6. Effect of Al ions on the lysosomal activity of cells at concentrations in the 4.5 x (Al4.5) to 9 x AC8h (Al9) range. 3. 7. Synergistic effect of mixtures of ions In Table 3 the effect of the single Zn and Al ions and their combinations are compared. When Al-Zn combination was used (Fig. 7) the reduction in the lysosomal activity was found even in the case of mixtures Al-Zn of 6 x AC8h (90%). It worth mentioning that 6 x AC8h is below the cytotoxic level, when single ions are used (Figs. 5 and 6). In the case of 9 x AC8h Al-Zn mixtures values close to 50 % of the control were found (Fig. 7). Interestingly, single ions at 7.5 – 15 x AC8h range did not show any cytotoxic effect. However the mixture of all the ions at 9x AC8h concentrations showed a reduction in the lysosomal activity to ca. 20 % of the control value (Table 3). % Lysosomal activity after exposure to different ions* Ions (Al) (Zn) (Mixture Al-Zn) (Mixture of all the ions) -----95.21 (0.65) 100.35 (1.58) 87.14 (4.97) 67.43 (2.25) 49.13 (1.98) ------------20.69 (1.63) Concentration 94.32 (3.07) 6xAC8h 84.08 (4.01) 7.5xAC8h 44.59 (5.75) 9Xac8h * Standard Errors are between brackets Table 3. Lysosomal activity of cells after exposure to single Zn and Al ions and their combinations. Fig. 7. Effect of Al and Zn ions on the lysosomal activity of cells. 4. DISCUSSION 4.1 Aluminium bronzes as dental materials Aluminium bronzes have appeared as economical substitutes of conventional gold rich alloys to fabricate crowns and bridges. (Eschler et al, 2003; Carvalho and Matson 1990) However, previous reports have shown a very low corrosion resistance and possible cytotoxic effects on surrounding cells. (Ardlin et al, 2009) Consequently, the widespread use of these dental alloys is a cause of great concern. Like other alloys, the corrosion rate of aluminium bronzes is dependent on their composition. However, it is well known that an alloy does not necessarily release elements in proportion to its composition. (Wataha, 2000; Tibballs and Erimescu, 2006) The difference in the corrosion rate of each component according to the composition of the copper-based alloys (Cu, Al, Mn, Fe and Ni in case of Orcast and NPG alloys) as well as the influence of the electrolyte composition (Elshahawy et al, 2009; Tibballs and Erimescu, 2006; Ardlin et al, 2009) yielding to different cytotoxic response have been previously shown. (Bumgardner et al, 2002; Ardlin et al, 2009) In agreement with previous results our data show that in the case of Orcast alloy the higher ion release was found for Al. As it was expected, our electrochemical data showed that the dissolution rate of CuBA is different from that of pure copper, being dependent on the pH and composition of the electrolyte (SS or CCM). Additionally the anodic current intensities were also dependent on the exposure period: immediately after the immersion current intensities were higher than after the different immersion periods in the electrolyte. In agreement with clinical tests (Arvidson et al, 1980; Arvidson and Wróblewski, 1978) the high initial release rate of metal ions from CuBA resulted in cytotoxic effects on the surrounding cells. These results seem to disagree with data that show no cytotoxic effect when the cells were exposed to single ions (except for Al) at concentrations in the AC8h to 30 x AC8h range. These data could be interpreted on the basis of a process controlled by the diffusion of ions. The study of the distribution of metal ion concentration in the different zones in order to describe and simulate qualitative the space/time variation of ion concentration is being carried out in our laboratory. 4.2. Synergistic cytotoxic effects of the combination of metal ions When the cytotoxicity of single ions were tested, Al cations showed a high cytotoxic effect for 9 x AC8h. A similar effect was shown in case of Zn when 36 x AC8h. Cytotoxic effects of Al ions have been previously reported. (Eisenbarth et al, 2004; Kopaci et al, 2002; Lima et al, 2007; Urania et al, 2001) However, to the best of our knowledge possible synergistic effect of some combinations of the ions released by aluminum bronze has not been analyzed. Our assays with Al-Zn combinations show synergistic effects when concentrations between 6 x and 9 x AC8h were used. Accordingly, the uptake of each ion (Al or Zn) may be interfered by the other yielding to a significant higher cytotoxic effect (synergism). Urania et al. (Urania et al, 2001) showed that when results obtained with concentrations of metal ions used singly or in combination were compared they observed that Zn was accumulated in cells at a significant higher concentration when used in combination with Cu. Additionally, a marked decrease in cell viability and protein content was found for this mixture. On the other hand, Fe and Zn can also interfere in other ions uptake processes (Mantha et al, 2011; Flemming and Trevors, 1989). It was suggested that the synergism of the mixture Cu + Zn was evident as the redoxactive metal Cu could enhance the Zn absorption in a living system (Stauber and Florence, 1990; Moriwaki et al, 2008). Furthermore this combination of Cu + Zn might also play a main role in the mixtures with other ions. In addition, synergic effects of mixtures of some metal ions (Cu, Fe, Ni, Cr ions) on oxidative DNA damage mediated by a Fenton-type reduction have been previously identified (Xu et al., 2011). Xu et al. (2011) made toxicological assays with individual, binary, ternary and quaternary mixture of four heavy metals (Cu, Pb, Zn and Cd) on embryos. Their results showed that in most of the binary combinations, the interactions were synergistic. Accordingly, our results revealed that when the osteoblastic cells were exposed to the overall mixture of ions at 9 x AC8h a higher cytotoxic effect than in the case of Zn-Al combination was found. Considering that each individual ion (except Al) did not show any cytotoxic effect up to 30 x AC8h concentration value, these results clearly indicate the dramatic influence of the simultaneous presence of several ions at concentrations close to 9 x AC8h on osteoblastic cell viability. Consequently, our results on cytotoxic effects in the vicinity of metal discs at AC values lower than toxic level can be interpreted considering that the cells in this region may be exposed, as a result of concentration gradients, to mixtures of ions that, even nontoxic as single ions, are cytotoxic in mixtures, due to synergistic effects. The difference in response to ions released from the alloys and salt solutions representing the ions released from the alloys reported by other authors (Messer and Lucas, 1999) may also be interpreted following this scheme. 4.3. Cellular response to metal discs within the cell culture and culture media with metallic salts. At this point it is interesting to complement the interpretation of some apparent inconsistencies detected by Messer and Lucas (1999) in the results of biocompatibility assays. They found that cellular functions were not similarly altered in response to ions released from the alloys and to their salts. They highlighted that salt solutions cannot be easily used to represent alloy cytotoxicity because ionic release from alloys is a complex process with a dose-time dependence. It should also be considered that when the concentration of the ions released is evaluated by atomic absorption spectroscopy the concentration of the samples measured for this analysis is the corresponding average concentration value, AC of the original concentration gradient. When salts or extracts are used to simulate the effect of ion release in cultures, the concentration is uniform and similar to the corresponding AC. There are no concentration gradients in these cases. Thus, Schmalz et al (1998) demonstrated that the results of experiences with salts and extracts were only slightly different. This concentration levels may be below the toxicity threshold and consequently no effect on cells are found. However, in experiments with discs, concentrations close to the discs are high and time dependent, reaching values markedly higher than the AC value, and exciding citotoxic threshold levels, mainly in the case of mixtures with synergistic effects. Thus, although the AC value measured by atomic absorption spectrophotometry is below the toxic threshold value, cytotoxic effects may be found near the metal disc leading to the decrease in cell viability. In the oral environment, changes in quantity and quality of saliva, diet, oral hygiene, polishing of the alloy, distribution of occulsal fouces, and burshing can also influence the rate of ions release. Although the release of copper, aluminium, nickel, manganese and iron remains far below the upper tolerable human intake levels (Lopez Alías, 2006) they may cause cytotoxic effects locally. Overall, different criteria have been applied when the cytotoxicity of metal ions is assessed. Some authors have suggested that complete materials should be used to evaluate the cytotoxicity of dental materials. Others consider that even such assays can assess the total cytotoxicity of a dental alloy, the evaluation of the toxicity of individual components is impeded. Importantly, present study demonstrated that experiments with dental alloys and the use of mixture of ions are highly applicable to evaluate possible synergic effects of ions and also space/time variation in cytotoxicity. CONCLUSIONS Results showed that the concentrations of the metal ions released by CuBA (average concentration: AC) cannot be predicted on the basis of the overall composition of this alloy. Higher concentrations than that of the copper base metal were found for Al, Zn, Ni and Fe released ions. An important cytotoxic effect (reduction in cell viability and in the size of colonies) was observed for cells in the surroundings of the metal disc. Experiments with individual salts of the metal ions at concentrations levels similar to those released by a 3 cm2 alloy after 8h (AC8h) exposure and with the mixture of all the salts did not show any effect on the cells. However aluminum, zinc and manganese ions at concentrations 6x, 36x and 60xAC8h, respectively, affected lysosomal activity. Importantly, a synergistic effect was found when Al-Zn mixtures of 6x, 7.5x, 9xAC8h were used. A stronger synergism was observed when the mixture of all ions at 9xAC8h concentrations was used, demonstrating that cell viability was also affected by the simultaneous presence of more than two ions. Cytotoxic effects in the vicinity of cell discs (zone A1) with the average AC levels of each ion lower than the cytotoxic threshold values could be interpreted through a diffusion controlled mechanism that could yield to concentration gradients, with concentrations levels several times higher than the AC value in the metal surroundings. The existence of concentration gradients may also contribute to the interpretation of apparent discrepancies reported by other authors when two different sources of metal ions are used: multiple ion salt solutions and samples of the dental alloys. The importance of the evaluation of the synergic cytotoxic effect of mixtures of ions when cytotoxic effects of alloys are analyzed is also highlighted. ACKNOWLEDGMENTS This work was supported by grants from: Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET) (PIP 0847), Agencia Nacional de Promoción Científica y Técnica (ANPCyT) (PICT 2010-BID 1779), Universidad Nacional de La Plata (UNLP), and Facultad de Ingeniería UNLP, Áreas Departamentales de Ingeniería Química y Mecánica (11- I129 and 11- I133). REFERENCES B.I. Ardlin, B. Lindholm-Sethson, J.E. Dahl, J Biomed Mater Res. 88B (2009) 465-473. K.Arvidson, R. Wróblewski, Share Scandinavian J Dental Res. 86 (1978) 200-205. K.Arvidson, M. Cottler-Fox, U. Friberg, J Dental Res. 59 (1980) 651-656. E.Borenfreud, J.A. Puerner. J Tissue Cult Methods 9(1984)7-9. J.D.Bumgardner, P.D. Gerard, W. Geurtsen, G. Leyhausen, J. Biomed Mater Res. 63 (2002) 214-219. J.D.Bumgardner, C.L. Lucas CL, J Dent Res. 74 (1995) 1521-1527. R.C. Carvalho, E. Matson, Rev Odontol Univ Sao Paulo. 4, 2 (1990) 13-118. R.G.Craig, C.T. Hanks, J Dent Res. 69 (1990) 1539-1542. E.Eisenbarth, D. Velten, M.M. Ullera, R. Thull, J. Breme, Biomaterials. 25 (2004) 5705-5713. W.Elshahawy, I. Watanabe, M. Koike, Dent Mater. 25, 8 (2009) 976-981. P.Y.Eschler, H. Lüthy, L. Reclaru, A. Blatter, O. Loeffel, C. Süsz, J. Boesch, European Cells and Materials. 5, 1 (2003) 49-50. C.A. Flemming, J.T. Trevors, Water Air Soil Poll. 44 (1989) 143-158. C.Fleury, A. Petit, F. Mwale, J. Antoniou, D.J. Zukor, M. Tabrizian, O.L. Huk, Biomaterials. 27 (2006) 3351-3360. N.P. Franken, H.M. Rodermond, J. Stap, J. Haveman, C. van Bree, Nature Protocols 1 (2006) 2315-2319. D.G.Granchi, E. Cenni, G. Ciapetti, J Mater Sci Mater Med. 9 (1998) 31-37. W.Geurtsen, J Dent Res. 82 (2003) 500-508. V.Grill, M.A. Sandrucci, M. Basa, R. Di Lenarda, E. Dorigo, P. Narducci, A.M. Martelli, G. Delbello, R. Bareggi, Arch Oral Biol. 42 (1997) 641-647. V. Grill, M.A. Sandrucci, R. Di Lenarda, M. Cadenaro, P. Narducci, R. Bareggi, A.M. Martelli, J Biomed Mater Res. 52 (2000) 479-487. C.A. Grillo, MA Reigosa, M. Fernández Lorenzo de Mele, Mutat Res 672 (2009) 45-50. O.L Huk., I.C. Catelas, F. Mwale, J. Antoniou, D.J. Zukor, A. Petit, J Arthroplast. 19 (2004) 84-87. A. Kapanen, J. Ilvesaro, A. Danilov, J. Ryhänen, P. Lehenkari, J. Tuukkanen, Biomaterials 23 (2002) 645-650. A. Kapanen, A. Kinnunen, J. Ryhänen, J. Tuukkanen J, Biomaterials. 23 (2001) 3341-3346. I.Kopaci, U. Batista, E. Cvetko, L. Marion, J Oral Rehabil. 29 (2002) 98-104. P.D.L Lima., D.S. Leite, M.C. Vasconcellos, B.C. Cavalcanti, R.A. Santos, L.V. Costa-Lotufo, C. Pessoa, M.O. Moraes, R.R. Burbano, Food and Chem Toxicol. 45 (2007) 1154-1159. R.L. Macchi, Dental materials. Pan American, Buenos Aires, Argentina (2000), 269p M.Mantha, L. El Idrissi, T. Leclerc-Beaulieu, C, Jumarie, Toxicol in Vitro. 25 (2011) 1701–1711. R.L.W. Messer, L.C. Lucas, Dent Mater. 15, 1 (1999) 1-6. K.Merrit, S.A. Brown, N.A. Shankey, J Biomed Mater Res. 18 (1984) 1005-1015. H.Moriwaki, M.R. Osborne, D.H. Phillips, Toxicol in Vitro. 22 (2008) 36-44. J.W. McGuiness, P.M. McInnes-Ledoux, E.F. Ferraro, J.C. Carr, Oral Surg Oral Med Oral Pathol. 63 (1987) 511-514. M.D. Pereda, M.A. Reigosa, M. Fernández Lorenzo de Mele, Bioelectrochemistry. 72, 1 (2008) 91-101. J.L. Stauber, T.M. Florence, Mar Biol. 105 (1990) 519-524. K. Stoffers, S. Strawn, K. Asgar, J Dent Res. 66 (1987) 205-207. J.E. Tibballs, R. Erimescu, Dent Mater. 22 (2006) 793-798. C. Urania, P. Melchiorettoa, F. Morazzonib, C. Canevalib, M. Camatinia, Toxicol in Vitro. 15 (2001) 497-502. J.C. Wataha, C.T. Hanks, R.G. Craig, Dent Mater. 8 (1992) 65-70. J.C. Wataha, C.T. Hanks, R.G. Craig, J Biomed Mater Res. 28, 4 (1994) 427-433. J.C. Wataha, J.B. Lewis, P.E. Lockwood, D.R. Rakic, J Oral Rehabil. 27 (2000) 508-516. J.C. Wataha, J Oral Rehabil. 83 (2000) 223-234. J.C. Wataha, S.K. Nelson, P.E. Lockwood, Dent Mater.17 (2001) 409-441. J.C. Wataha, P.E. Lockwood, A. Schedle, M. Noda, S. Bouillaguet, J Oral Rehabil. 29 (2002) 133-139. X. Xu, Y. Li, Y. Wang, Y. Wang, Toxicol in Vitro. 25 (2011) 294-300.