Toxicity evaluation of manufactured CeO2 nanoparticles before and after alteration: combined physicochemical and whole-genome expression analysis in Caco-2 cells
BMC Genomics volume 15, Article number: 700 (2014)
Engineered nanomaterials may release nanosized residues, by degradation, throughout their life cycle. These residues may be a threat for living organisms. They may be ingested by humans through food and water. Although the toxicity of pristine CeO2 nanoparticles (NPs) has been documented, there is a lack of studies on manufactured nanoparticles, which are often surface modified. Here, we investigated the potential adverse effects of CeO2 Nanobyk 3810™ NPs, used in wood care, and their residues, altered by light or acid.
Human intestinal Caco-2 cells were exposed to residues degraded by daylight or in a medium simulating gastric acidity. Size and zeta potential were determined by dynamic light scattering. The surface structure and redox state of cerium were analyzed by transmission electronic microscopy (TEM) and X-ray absorption spectroscopy, respectively. Viability tests were performed in Caco-2 cells exposed to NPs. Cell morphology was imaged with scanning electronic microscopy. Gene expression profiles obtained from cells exposed to NPs before and after their alteration were compared, to highlight differences in cellular functions.
No change in the cerium redox state was observed for altered NPs. All CeO2 NPs suspended in the culture medium became microsized. Cytotoxicity tests showed no toxicity after Caco-2 cell exposure to these various NPs up to 170 μg/mL (24 h and 72 h). Nevertheless, a more-sensitive whole-gene-expression study, based on a pathway-driven analysis, highlighted a modification of metabolic activity, especially mitochondrial function, by altered Nanobyk 3810™. The down-regulation of key genes of this pathway was validated by qRT-PCR. Conversely, Nanobyk 3810™ coated with ammonium citrate did not display any adverse effect at the same concentration.
The degraded nanoparticles were more toxic than their coated counterparts. Desorption of the outside layer was the most likely cause of this discrepancy in toxicity. It can be assumed that the safe design of engineered nanoparticles could include robust protective layers conferring on them greater resistance to alteration during their life cycle.
The use of nanoparticles (NPs) has increased significantly during the last decade in several areas such as computer science, chemistry, cosmetics and pharmaceuticals. There is an urgent need to verify their harmlessness in relation to human health and the environment. Cerium oxide (CeO2) NPs are one of the most widely used types, for UV protection in paints or as fuel additives [1, 2]. These NPs are usually surface modified to be incorporated into the final commercialized products. Contrary to toxicity studies regarding pristine CeO2 NPs, very few studies have focused on manufactured nanoparticles, which are often surface treated to improve their dispersion in liquids. In recent years, CeO2 NPs have been shown to induce loss of viability  and apoptosis  in human lung cells through ROS production, as well as DNA and chromosome damage to human dermal cells . However, these results are controversial. Xia et al. showed a lack of toxicity of CeO2 NPs and a protective effect against exogenous ROS . This result is in agreement with the neuroprotective effect of CeO2 nanoparticles observed by Schubert et al. . So far, a clear answer to the question as to whether engineered CeO2 nanoparticles are toxic or cross biological barriers cannot be provided and more work is required. In addition, these studies focused mainly on inhalation rather than oral exposure, which is also a potential route. To our knowledge, the toxicity of CeO2 NPs to intestinal cells was evaluated only recently by B. Gaiser et al. . The authors suggested that both micro- and nanosized CeO2 NPs can be taken up by Caco-2 cells, but with little biological consequence, although they suggested that further work would be required to investigate this in more detail. All of these studies focused on the toxicity of pristine CeO2 NPs, i.e. at the beginning of the NP’s chain value. However, the NPs that spread in the environment are likely to be degradation residues of CeO2-based nanomaterials. Exposure to the environment (UV, water and air contact …) may alter the physicochemical properties of surface-modified CeO2 NPs, such as the chemical structure of the surface, size, shape, and dispersion state, which are important parameters for toxicity. After ingestion, stomach acidity can also alter the physicochemical properties of surface-modified CeO2 NPs, and their toxic properties. For instance, Wang et al. described an increase in CdSe NP toxicity in intestinal cells after acid treatment, due to degradation of the PEG protective layer .
Our study focuses on CeO2-based nanomaterials at several stages of the product life cycle. CeO2 NPs usually refer to uncoated NPs with UV filter properties. However, CeO2 NPs are often formulated prior to use as outdoor paint adjuvants, i.e. the commercialized product, Nanobyk 3810™ (named NB in the text), from the Byk Company. This Nanobyk™ formulation comprises a core of CeO2 NPs with a triammonium citrate coating that improves their dispersion in water and paint [10, 11]. The question arises as to whether, during its life cycle, especially by exposure to daylight, this material transforms into a more toxic form for living organisms and the environment.
This work aims to evaluate the relative toxicity of manufactured CeO2 Nanobyk™ NPs (NB) compared with their degraded counterparts. Two alteration protocols were used. Firstly, extreme and long-term environmental conditions of aging (100% hygrometry and permanent sunshine) were reproduced, leading to a light-degraded residue (NB-DL). Secondly, gastric degradation was mimicked using a simulated gastric medium, to generate an acid-degraded residue (NB-DA). Surface-untreated (pristine) CeO2 NPs from Rhodia were used as a comparative material.
Physicochemical properties (e.g., shape, size, aggregation state, zeta potential and crystal structure) were determined using dynamic light scattering (DLS) coupled to laser Doppler microelectrophoresis for zeta potential measurement, and transmission electron microscopy (TEM). The surface structure and redox state of cerium (Ce4+ versus Ce3+) were analyzed by X-ray absorption spectroscopy (XAS) [5, 12].
We used the Caco-2 cell line as a human intestinal epithelium model. This cell line has been extensively characterized and shown to exhibit a faithful representation of in vivo structural characteristics. At the molecular level, these cells mirror the differentiation of human intestinal cells [13, 14].
We used two viability tests to determine toxic concentrations of these nanoparticles in Caco-2 cells (ATP intracellular measurement and XTT test). Several tests based on different principles are often necessary because NPs may sometimes interact with the test principle [15, 16]. The first cytotoxicity test is one of the most sensitive toxicity assays because it is based on the measurement of ATP, which reflects the energy state of the cell, even before any damage to membrane integrity occurs. The second, and more usual, test (XTT) is based on the activity of mitochondrial enzymes. These tests are routine tests attesting to the presence of dead cells. Nevertheless, some deleterious effects may occur before cell death (inflammation, sensitization, oxidative stress). This is why we also used toxicogenomics, meaning analysis of the whole genomic expression with human pangenomic microarrays to obtain an overview of intracellular events triggered by these various NPs. Additionally, using the same methodology, we also examined the adverse effects elicited by pristine CeO2 NPs as comparative material. Hydrogen peroxide was used as positive control, as its effect in Caco-2 cells has been described . We compared the expression profiles of cells exposed to these various particles before and after alteration, using a low concentration (20 μg/mL) about eight times lower than that producing the first visible loss of viability by XTT test. We used scanning electronic microscopy (SEM) to visualize potential adsorption of aggregates onto the cell surface. This multipronged approach gives more certainty and coherence to the acquired data.
Physicochemical behavior of (un)altered Nanobyk™ NPs and pristine CeO2NPs
Unaltered Nanobyk™ NPs and pristine CeO2 NPs were characterized in pure water. In both cases, TEM showed well-crystallized clusters of cerianite with an inter-reticular distance (dhkl) measured at around ~3.2 Å (close to the d111 of CeO2). These clusters were pseudospherical with diameters of 3 ± 1 nm (average of 50 measurements) (Figure 1). In the stock suspension, the pristine CeO2 NPs and unaltered Nanobyk™ NPs were colloidally stable, with average hydrodynamic diameters (Dh) of ~7 nm. At pH ~ 7 ± 0.1, the zeta potential of the Nanobyk™ NPs was negative (−45 ± 5 mV) compared with the positive zeta potential of the pristine CeO2 NPs (28 ± 2 mV). After both environmental (light) and gastric (acidic) degradation, the zeta potential of the Nanobyk™ NPs increased (−28 ± 2 mV and −19 ± 2 mV, respectively, at pH 7 ± 0.2). No change in the Ce redox state was observed between the unaltered Nanobyk™, Nanobyk DL and Nanobyk DA (Additional file 1: Figure S1).
The dispersion of NPs has a crucial impact on toxicity. We used DLS to measure the apparent hydrodynamic diameters of NPs in different media. In water, the pristine CeO2 NPs and unaltered Nanobyk NPs were dispersed and stable with average hydrodynamic diameters (Dh) of 7 nm. In culture medium, with or without serum, they formed aggregates above 1 μm size. Light- and acid-degraded NPs formed similar aggregates whatever the medium (water, serum-free medium and medium supplemented with 10% FCS). In the presence of 10% serum, in our hands, DLS analyses were especially unreliable, whatever the NPs and concentrations, giving average sizes approaching 2 μm with particle dispersion indexes close to 1. In serum-free medium, the mean hydrodynamic diameters were 1580 ± 1000 nm, 1030 ± 370 nm, 1300 ± 190 nm, and 2200 ± 500 nm for the NB, NB-DL, NB-DA, and the pristine CeO2, respectively. It is noteworthy that the samples were not sonicated before any of the toxicity assays.
The studies were conducted on the well-established Caco-2 cell line, differentiated for 21 days. The integrity of the cell layer was assessed by measurement of the transepithelial electrical resistance (TEER), stabilized at 500 ohms.cm2 after 21 days. We performed two cytotoxicity tests at two exposure times, 24 h and 72 h, to take into account the kinetic parameters. As shown in Figure 2, with the ATP assay (Left side), the presence of CeO2 NPs did not induce adverse effects on Caco-2 cells after 24 h or 72 h exposure, even at high concentration (170 μg/mL). The XTT assay (Right side) confirmed the lack of apparent toxicity of Nanobyk NPs and pristine cerium NPs in Caco-2 cells. For degraded Nanobyk NPs (NB-DL and NB-DA) only mild toxicity was observed using the XTT test, and only at the highest concentration (170 μg/mL) after 72 h exposure.
Cell morphology after exposure
We visualized cells with SEM. Caco-2 cells exposed for 72 h to 170 μg/mL Nanobyk-type NPs did not show any alteration in density. The microvilli were also clearly visible (Additional file 2: Figure S2). These observations confirmed the absence of visible toxicity of Nanobyk NPs and indicated that, if an effect exists owing to exposure to degraded NB, this effect is small enough not to induce any drastic changes in cell morphology. It is noteworthy that this does not exclude any possible metabolic modification. Nevertheless, clear spots identified as CeO2 deposits were clearly visible on the surface of the plasma membrane, especially for NB-DL (Figure 3).
Caco-2 cells were exposed to Nanobyk, Nanobyk DL, Nanobyk DA and pristine CeO2 for 72 h at 21.25 μg/mL. Cells were also exposed to hydrogen peroxide as a positive control. Agilent Oligo microarrays spotted with 4 x 44,000 probes were hybridized in quadruplicates with RNAs originating from cells exposed to NPs, or from unexposed cells (for exact design details, see Methods). Additional file 3: Figure S3 represents the scatter plots of the raw fluorescence intensities of genes filtered on the threshold intensity signal of the microarray experiments (n = 4). The scatter plot obtained for Nanobyk NPs versus control 1 was very similar to the control scatter plot representing the raw intensities of genes obtained from untreated cells from two different cultures (control 2 versus control 1) giving the false positive rate (5 genes). The exact number of significantly altered genes (fold change ≥ 1.5, p-value <0.05) in each probe set is reported in Table 1. The exhaustive list with gene names and fold changes is shown in Additional file 4: Table S1 under Supporting Information (see Additional file 4).
Cells exposed to NB showed almost no change in their gene expression, only 13 genes having significantly modified expression. Conversely, cells exposed to degraded NPs had a different scatter plot from the control scatter plot, and had 344 and 428 modified genes for NB-DL and NB-DA, respectively, with 37 common genes listed in Additional file 5: Table S2 under Supporting Information, (see Additional file 5). Cells exposed to pristine (surface-untreated) CeO2 NPs displayed much stronger deregulation of their gene expression, with 1643 modified genes. Furthermore, a positive-control scatter plot was obtained with cells exposed to hydrogen peroxide for 24 h at 20 μM (9307 modified genes).
Biological analysis of the transcriptome
The lists of altered genes were then processed using Ingenuity Pathways Analysis to investigate a possible relationship between altered genes and mechanisms of toxicity.
For pristine CeO2 NPs, the main altered functions were cellular growth and proliferation (274 genes) and cell death (265 genes), as shown in Figure 4. Contrarily to pristine CeO2 NPs, the surface-treated NB NPs did not alter any specific cellular function (not shown in Figure 4, as only 13 genes are altered), thus proving the efficiency of the protective triammonium citrate layer. The NB nanoparticle residues of degradation by light or acid altered similar functions to pristine CeO2 NPs, although in a very moderate way, given the number of altered genes. The distribution per function for NB residues is shown in the enlarged part of Figure 4. For NB-DL, the main altered functions were cellular growth and proliferation (51 genes), cellular development (35 genes), small molecule biochemistry (26 genes), cellular assembly and organization (25 genes), cell cycle (24 genes), cellular function and maintenance (24 genes) and cell death (20 genes). Other functions counted for less than 15 genes each.
For NB-DA, the altered functions were molecular transport (53 genes), small molecule biochemistry (45 genes), cellular assembly and organization (32 genes), nucleic acid metabolism (23 genes), cellular function and maintenance, lipid metabolism and protein synthesis (22 genes each) and cell death (21 genes). Other functions counted for less than 15 genes each.
Canonical pathways analysis
If we look more precisely at the main common molecular pathways definitely impacted by these different NPs (Figure 5), pristine CeO2 NPs induced mitochondrial dysfunction through the underexpression of 27 genes of complexes I, III, IV and V, listed in Table 2 Part A. Interestingly, the NB-DA residue also induced mitochondrial dysfunction by underexpressing 10 genes of the complexes I, II, III, IV and VI, listed in Table 2 Part B. Nevertheless, in the case of NB-DA this pathway was affected to a lesser extent. The same trend was observed with NB-DL, which downregulated 3 genes in this pathway, reported in Table 2 Part C.
qRT-PCR validation of the microarray data focused on mitochondrial dysfunction
Validation of the microarray data was confirmed by quantitative RT-PCR on 8 genes belonging to complexes of mitochondrial respiratory chain. The compared fold changes obtained with microarray and with qRT-PCR were reported in Table 3. All mRNAs were downregulated with both techniques, with a good level of significance (p < 0.05).
Contrary to the toxicity studies regarding pristine CeO2 NPs, very few studies have focused on engineered nanoparticles, which are often surface treated for better dispersion in liquid products. However, these particles can be degraded in the environment during their life cycle. Moreover, although the toxicity of pristine nanoparticles via inhalation is well documented [3, 18, 19], only a few evaluations of toxicity associated with oral exposure have been carried out . Here, we investigated the potential toxic effects on the intestine of Nanobyk 3810™ NPs, used as long-term UV protection for wood, and their degradation residues, as compared with pristine CeO2 NPs. We considered two degradation scenarios: i) due to environmental conditions, and ii) due to stomach acidity. Caco-2 cells were used for toxicity evaluations and their differentiation was evaluated with the measurement of transepithelial resistance.
Following both environmental or acidic degradation in water, the NB surface becomes less negatively charged at physiological pH than the initial NB (zeta potential −28 ± 2 mV and −19 ± 2 mV for NB-DL and NB-DA, respectively, compared to −45 mV for NB). These negative surface charges are attributed to the negatively charged citrate capping at this pH. Indeed, citrate is a tricarboxylic acid with three dissociated protons (pKa1 = 3.13, pKa2 = 4.76 and pKa3 = 6.40) . Consequently, partial desorption of the citrate layer during alteration will decrease the negative charges at the surface of the Nanobyk™, as already described . While the Nanobyk and the pristine CeO2 NPs have hydrodynamic diameters of 7 ± 1 nm in a dispersed state, strong aggregation occurs in the culture medium, with and without 10% FCS. Serum proteins usually help the dispersal of the NPs , but for very small NPs with hydrodynamic diameters less than 10 nm the bonds to proteins are so weak and labile that most of the NPs exchange quickly, which favors aggregation, as has been described recently in our laboratory by Liu et al. . Using a culture medium supplemented with 10% FCS and containing 60 μg/mL CeO2 NPs, NP distribution with the protein population was analyzed by size exclusion chromatography and ICP-MS, which showed that 90% of the CeO2 NP population was eluted in the dead volume as homo aggregates. This is consistent with the results obtained by SEM showing adsorbed NP aggregates on the cell membrane. The hydrodynamic diameters of all NPs tested, including NB-DL and NB-DA, in the cell culture medium are microsized, between 1 and 2 μm, with zeta potentials around −15 mV, leading to strong aggregation, and coherent with published data [18, 23, 24].
Through two different toxicity assays (ATP and XTT), Caco-2 showed no loss of viability after exposure to up to 170 μg/mL over 72 h for Nanobyk 3810™ and pristine CeO2 NPs. For degraded Nanobyk NPs, a slight effect (27% loss of viability) was observed for the highest concentration (170 μg/mL) after 72 h with the XTT test, but not with the ATP tests, for NB-DL and NB-DA. ATP and XTT tests are not based on the same principle. XTT is directly based on the enzymatic activity of succinate dehydrogenase, essential to mitochondria. We showed that this enzyme was down regulated in our dataset. ATP test measures the total amount of intracellular ATP that is not decreased in a so sensitive way. This explains why the sole XTT test is disturbed by those NPs. This last test tends to indicate that altered Nanobyk NPs induce a slight change in mitochondrial function. It should be also noted that the XTT test, by induction of a soluble formazan species, does not suffer from the possible interference with NPs frequently described with the MTT assay. This known bias is due to the formation of insoluble MTT formazan, which is often entwined with NP fibers or complexes that inhibit its resolution by the solvent . None of the tested nanoparticles induced drastic changes in cellular aspect as depicted in Additional file 2: Figure S2, excepted deposits on cell membrane, suggesting that the effect was probably a modification of the internal metabolic activity. It is possible that some signaling cascades may be triggered by interaction with membrane proteins such as protein-G coupled receptors .
We did not notice any evolution of the redox state (i.e. potential reduction of Ce4+ to Ce3+) of Ce atoms localized at the surface of the NPs after alteration in water. The shape of XANES spectra at the Ce L3-edge, and the position of the edge, are usually easily distinguished for Ce3+ and Ce4+ reference compounds: one absorption edge at 5729 eV for Ce3+ and a double peak at 5733 eV and 5740 eV for Ce4+ (Additional file 1: Figure S1). Consequently, XANES, used to detect any slight change in the redox state of CeO2, indicated no Ce3+ in our suspensions.
Standard toxicological methods in vivo cannot unravel the mechanisms of action of toxicants. Some in vitro methods are able to do so, but rarely at sublethal doses. Conversely, toxicogenomics is a methodology capable of detecting potential changes in cellular and molecular functions at low dose, and constitutes an alternative for assessing the toxicity of nanomaterials . In particular, microarray-based transcriptional profiling is a powerful tool for monitoring altered cellular functions and pathways (i.e. oxidative stress, apoptosis, hypoxia, etc.) under the action of toxicants. Gene expression studies, through a large number of altered genes, provide a wealth of information for sketching the intracellular mode of action of toxic substances [28, 29]. These results usually lead to the generation of new hypotheses about the specific toxicity of the substances concerned, then allowing targeted in vitro or in vivo experiments. The overall number of altered genes is a very good indicator of the level of cellular disturbance induced by a toxic compound.
The cells were exposed to 21.25 μg/mL of various NPs for 72 h, a concentration about eight times lower than that producing the first visible loss of cell viability at 72 h with the XTT test. This exploratory concentration was chosen in the absence of any oral reference dose for cerium oxide nanoparticles. In the current study, toxicogenomic results showed that, by exposure to NanoByk NPs capped with ammonium citrate, Caco-2 cells were almost unaffected, as only 13 genes were altered out of 44,000 transcripts (Table 1). On the contrary, by exposure to pristine CeO2 nanoparticles used as the reference material in the same conditions, cells underwent a strong alteration of gene expression, with 1,643 significantly differentially expressed genes. In short, capping nanoparticles provides a very good protection against adverse cellular effects. On the other hand, light- or acid-degraded Nanobyk NPs moderately altered the transcriptome of Caco-2 cells, with 344 and 428 modified genes, respectively, including 37 common genes (Additional file 5: Table S2). These alterations were much less important than those obtained when cells were exposed to pristine CeO2 NPs at the same concentration (1,643 genes). For instance, cell death was more highly activated for CeO2 NPs (265 genes) than for NB-DL and NB-DA (about 20 genes each). Otherwise, we noted that there was no cytokine production (chemokines or interleukins), indicating an absence of proinflammatory response with all the NPs tested.
To identify the mechanisms involved, we analyzed the distribution of altered genes per function, as defined in Gene Ontology (Figure 4). Radar plots may help here to apprehend the complexity of toxicity, both in terms of amplitude and effect. This results in a specific pattern representing the toxicity of each compound. Graph overlay of several products allows the visual comparison of their respective toxicities. Once again, the magnitude of the effect is given by the number of altered genes in a given function. For NB-DL, as for CeO2 NPs, the main altered functions were similar: cellular growth and proliferation (51 vs. 274 genes), cellular development (35 vs. 159 genes), cell death (20 vs. 265 genes) and small molecule biochemistry (26 vs. 140 genes). This may suggest that their modes of toxic action are similar. For NB-DA, the main altered functions related to molecular transport (53 genes) and small molecule biochemistry (45 genes). The functional mechanisms of toxicity were slightly different between the two residues, although this type of analysis is more informative with a higher number of genes. Small molecule biochemistry was an altered function in all cases.
Although the functions provide valuable information on the actions of the involved genes (transport, cell growth, etc. ..), the pathways help in understanding, in a faster and more extensive manner, the interactions between these genes themselves and the cellular mechanisms to which they belong. In the present study, pristine CeO2 NPs greatly disturbed the EIF-2 signaling pathway by downregulating the expression of more than 90 ribosomal proteins (S and L type), with a strong overall impact on protein synthesis (Figure 5). This result was consistent with the results of L. Benameur , where pristine CeO2 NPs triggered intracellular damage, such as the disruption of antioxidant systems (GSH, SOD, GPx, ascorbate), and impacted on protein synthesis in general.
Comparison of the common canonical pathways disturbed by pristine CeO2 NPs and degraded NB NPs essentially showed that they all disturbed mitochondrial functions and the oxidative phosphorylation pathway. Oxidative phosphorylation is the mitochondrial process by which ATP is formed as a result of the transfer of electrons from NADH or FADH2 through a series of electron carriers to oxygen. Consequently, this pathway is modified as a result of mitochondrial dysfunction (Figure 6). The downregulation of some key genes of oxidative phosphorylation was validated by qRT-PCR (Table 3).
This point confirms the results obtained above with the XTT test, which involved the mitochondrial enzymatic process. Moreover, the succinate dehydrogenase complex is clearly underexpressed by NB-DL and NB-DA (SDHB, SDHC and SDHD) whereas the NADH dehydrogenase complex (NDUFA, NDUFB and NDUFS) is downregulated by pristine CeO2 NPs. This impairment is, however, visible by toxicogenomics at a concentration divided by 8 (21.25 μg/mL) compared to the XTT test (170 μg/mL). This proves that toxicogenomics is more sensitive, while at the same time being informative about the molecular actions of toxic substances. Interestingly, although the same pathway was activated, there were, stricto sensu, no common genes altered by pristine CeO2 and NB-DA or NB-DL in the mitochondrial dysfunction pathway as reported in Table 2. Consequently, here, we demonstrated the interest of a pathway-driven analysis compared to the usual gene-driven analysis. In other words, looking at the whole picture is more informative than looking only at key genes.
In addition, these results were perfectly consistent with data obtained by D.A. Pelletier at al.,  who investigated the effects of cerium oxide NPs on bacterial growth and viability in E. coli, using microarray technology. These authors highlighted concomitant low levels of expression of succinate dehydrogenase and cytochrome b terminal oxidase genes. This indicates that cerium NPs alter electron flow and the respiratory chain in mitochondria. P. Rozenkranz et al. also demonstrated that pristine CeO2 NPs decreased mitochondrial activity in H4IIE cells .
In the case of the partial or total dissolution of the triammonium citrate layer of NB, the CeO2 core becomes exposed. A lack of effect of solubilized ammonium citrate can be assumed since this compound is totally metabolized by most cells in the urea (ammonium) and Krebs (citrate) cycles. Owing to the presence of oxygen vacancies on its surface, and to the self-regenerative cycle of its dual oxidation states, CeO2 can scavenge ROS in biological systems. Indeed, when the ratio Ce3+/Ce4+ falls, the scavenging capabilities increase . Through this property, altered NB adsorbed onto the cell membrane may interact with molecules such as membrane receptors, as suggested by Lee et al. , or other molecules, to trigger cell responses via catalytic properties of bare CeO2. This can only be a low level response because such interactions likely occur only at nanosized spots.
We showed that the properties of residues of Nanobyk™ nanoparticles tend to be similar to those of pristine CeO2 nanoparticles, and different from unaltered Nanobyk™. Consequently, cells exposed to light- or acid-degraded Nanobyk™ were exposed to nanoparticles having surface properties that were closer to those of pristine nanoparticles. The external layer had an efficient protective effect towards toxicity, as we recently observed elsewhere for engineered titanium dioxide NPs including an aluminum oxide protective layer . However, when this layer was altered, the toxic effects, visible by toxicogenomics, increased. Acid alteration of nanoparticles was more severe than light alteration, with regards to the respiratory chain. Macroscopic measurements revealed that all of these NPs were aggregated with identical zeta potential in the culture medium. Thus, the surface properties are important parameters for the toxicity of nanoparticles, whatever their aggregation state. This study examined the acute effects of engineered cerium oxide nanoparticles, which were very moderate. However, the question remains as to their long-term effects: this is another issue to be addressed.
The capping layer of Nanobyk 3810™ used in outdoor paints has an efficient protective effect against toxicity for intestinal cells. The alteration of this layer, by light or acidic treatment, causes some toxic effects similar to those induced by pristine CeO2 nanoparticles. Using toxicogenomics, we found a modification of cell metabolism, especially an alteration of mitochondrial function by underexpression of essential enzymes of the cellular respiratory chain, caused by these altered nanoparticles. The modification of engineered nanomaterials by the environment may increase their toxicity. However, the conclusions regarding cellular toxicity should not be confused with the conclusions on the risk due to these NPs. If the toxicity observed in Caco-2 cells with degraded nanoparticles is slightly higher than that observed with the initial, coated nanoparticles, the risk for humans (dose x exposure) is clearly not increased, as the highest concentrations to which humans may be exposed are currently 100,000 times lower than the concentrations tested . Nevertheless, special care should be taken in designing new nanoparticles, so that they do not transform into more toxic compounds. It can be assumed that a safer design of nanoparticles might include robust protective layers conferring on them more resistance to alterations during their life cycle.
Two protocols for NP alteration of the Nanobyk™ (BYK Company) were used in this study. These conditions reproduce extreme and long-term environmental conditions of aging (100% hygrometry and permanent sunshine). Before and after this process, a sample of the suspension was centrifuged (200,000 g) and freeze-dried for fine structural analysis . A Nanobyk™ stock suspension was diluted in milliQ water at 220 mg/mL. Firstly, 500 mL of this suspension was irradiated under artificial daylight for 112 days using OSRAM HQI-BT lamps (E40, 400 W) with a uniform spectral intensity between 425 and 650 nm, and under continuous stirring (100 rpm). A 4 mg/mL stable stock suspension of light-degraded Nanobyk™ (NB-DL) was obtained after 4 months, the time necessary to reach a stable conductivity and pH. This stock suspension of NB-DL was then diluted in a culture medium to obtain the exposure concentrations. Secondly, gastric degradation of the Nanobyk 3810™ was mimicked using a simulated gastric medium (0.2% NaCl, HCl, pH = 1) for 3 h at 37°C . This solution was then neutralized using NaHCO3. The stock suspension obtained (NB-DA, 2 mg/mL) was then diluted in the culture medium to obtain the exposure concentrations.
All concentrated suspensions were prepared in culture medium and allowed to be in contact with the medium prior to being diluted to exposure concentrations.
Physicochemical characterization of CeO2-based nanomaterials
The size, shape and mineralogy of Nanobyk™ NPs before and after alteration, as well as of pristine CeO2 NPs (originating from Rhodia), were characterized by high-resolution TEM, using a JEOL 2010 F operating at 200 kV. Samples were prepared by evaporating a droplet of the suspension on a carbon-coated copper grid at room temperature. The aggregation states of the nanoparticles were measured by DLS (n = 3) in pure water and in the culture medium, with and without 10% FCS, using the Zetasizer nano ZS (Malvern Instruments Ltd, UK). The zeta potential was also measured on the same instrument. The crystal structure and Ce oxidation state of CeO2 NPs and Nanobyk™ NPs were monitored on the atomic scale by X-ray absorption spectroscopy at the Ce L3-edge (5723 eV). Experiments were carried out in transmission mode on the ELETTRA synchrotron (Trieste, Italy) on the XAFS 11.1 beam line . Before and after aging, the suspension was centrifuged (200,000 g) and freeze-dried. The powders were then diluted in PVP and pressed into thin pellets. The spectra were compiled from the merging of three scans, and the energy was calibrated using a standard reference CeO2. XANES (X-ray absorption near-edge structure) data were obtained after performing standard procedures for pre-edge subtraction, and normalization using the IFEFFIT software package .
Cell culture and exposure conditions
Caco-2 cells (ATCC, Manassas, VA, US) were cultured in Eagle’s Minimum Essential Medium supplemented with 10% FCS (LGC Standards, Middlesex, UK) and penicillin/streptomycin (100 μg/mL) in a humidified incubator at 37°C, and 5% CO2. The cells were used between passages 20 to 40. The cells were passaged weekly at a seeding concentration of 6x103 cells/cm2 and the medium was changed three times per week.
Measurement of transepithelial resistance (TEER)
For TEER measurements, Caco-2 cells were seeded at a density of 5×104 cells per well in 12 Transwell culture plate inserts. MEM supplemented with 10% FCS was added to the apical and basolateral chambers and replenished three times a week. Cultures were confluent at 4 days and stabilized maximum resistance values were reached after 21 days. Transepithelial specific resistance was measured at 37°C using an STX2 electrode with an EvomX recorder (WPI). Blanks (inserts without cells but containing medium) were used to determine baseline values of electrical resistance. Results were expressed in ohms.cm2. Each experiment was repeated three times and three measurements were made for each culture plate insert.
Caco-2 cells were grown in 96-well plates and differentiated for 21 days. The cells were exposed for 24 h or 72 h to serially diluted concentrations of CeO2 NPs (21.25, 42.5, 85, and 170 μg/mL, 100 μL per well). Cells were washed with PBS and cell viability was determined by the ATP test as specified by the supplier (CellTiter-Glo luminescent cell viability Assay, Promega). Briefly, 100 μL kit reagent were added per well and the plate was shaken for 10 min at RT before measuring bioluminescence (LUMIstar Galaxy, BMG). Hydrogen peroxide (2.5 mM, 1.25 mM, and 0.625 mM) was used as a positive control.
Caco-2 cells were grown in 96-well plates and differentiated for 21 days. The cells were exposed for 24 h or 72 h to serially diluted concentrations of CeO2 NPs (21.25 to 170 μg/mL, 100 μL per well). Cells were washed with PBS and cell viability was determined by the XTT test as specified by the supplier (In Vitro toxicology assay kit XTT based, Sigma-Aldrich). Briefly, 20 μL kit reagent were added per well and the plate was incubated for 2 h at 37°C before reading absorbance at 450 nm and 690 nm (Multiscan Spectrum, Thermo Electron Corporation). Hydrogen peroxide (2.5 mM, 1.25 mM and 0.625 mM) was used as a positive control.
Scanning Electron Microscopy (SEM)
Caco-2 cells were seeded at 5×104 cells/cm2 in culture medium on clear Millicell-24 Cell Culture Insert Plates with a polyethylene terephthalate (PET) membrane (Millipore) for SEM observation, and allowed to differentiate for 21 days in a 5% CO2 incubator. The cells were exposed to highly concentrated NB-type CeO2 NPs (170 μg/mL). After 72 h, the cells were washed three times with PBS, fixed with 5% glutaraldehyde in 0.1 M cacodylate for 1 h at 4°C, then washed again twice with distilled water and dehydrated in graded ethanol baths (35, 70, 85, 95 and 100%). Finally, the cells were dehydrated in HMDS (SPI-Chem™) before examination by SEM. The samples were metallized by deposition of carbon (evaporation of braided carbon fiber (Agar scientific Stansted, UK) then analyzed on Balzers MED010 (Balzers Union, Lichtenstein).
Microarrays and gene expression analysis
For microarray experiments, the cells were seeded in 6-well plates (to collect sufficient amounts of RNA) in the above medium at 5 × 104 cells/cm2 and allowed to differentiate for 21 days. The cells were exposed to 21.25 μg/mL for 72 h of all types of CeO2 NPs (3 mL/well), in duplicate. The cells were also exposed to hydrogen peroxide for 24 h at 20 μM, as a positive control. Control duplicates were achieved in the vehicle. Each condition of exposure to NPs was compared with a control, i.e. untreated cells (control 1 for NB and NB-DL, control 2 for NB-DA, control 3 for hydrogen peroxide and pristine CeO2). The cells were washed extensively to avoid co-extraction of nucleic acids with NPs adsorbed onto the cell surface, collected with trypsin and washed with PBS. The cells were centrifuged and RNA extracted using the RNeasy kit (Qiagen). The RNAs were quantified with the Nanodrop 1000 and their qualities analyzed on an Agilent Bioanalyzer 2100. The RNAs were amplified and labeled with cyanine-3 fluorophore using a QuickAmp kit (Agilent), according to the supplier’s protocol. The efficiency of fluorescent labelling was controlled by UV spectroscopy (Nanodrop 1000) before hybridization on commercial Agilent oligo microarrays (Human V1 4X 44 K) in technical duplicates.
The 44,000 spots represent probes of the whole human genome, including redundancy. The microarrays were scanned with a GenePix 4000B (Axon Instrument Inc., Forster City, CA) in one-color mode at 532 nm and 5 μm resolution. Each condition of exposure to NPs, as well as controls, led to four hybridizations (two biological replicates and two technical replicates). We used Agilent microarrays with four independent genomes per chip (4 × 44,000 probes), thus 8 microarrays are sufficient to perform 32 hybridizations.
In this experimental design, six analyses were conducted: a) control 2 versus control 1, as the experimental negative control, b) hydrogen-peroxide-exposed cells versus unexposed cells (named control 3), as the experimental positive control, and c) surface-untreated (pristine) CeO2-NP-exposed cells versus unexposed cells (named control 3), d) NB-exposed cells versus unexposed cells (named control 1), e) NB-DL exposed versus unexposed cells (named control 1) f) NB-DA exposed versus unexposed cells (named control 2). For each analysis, eight raw fluorescence data files were obtained after scanning, which corresponded to four treated cells and four control cells. All files (n = 32) were submitted to GeneSpring software GX11 (Agilent Technologies) for statistical analysis.
Concerning the statistics methodology, we used a widespread method for determining the significance of the change in gene expression [28, 35]. The raw data were first normalized using the percentile shift 75 normalization method. The normalized data were then filtered on the basis of spots present on 100% of the slides in one of two conditions (treated NPs or control). Only spots detected with at least 70% of their pixels above the threshold intensity signal (set to the median background plus two standard deviations) were selected. From the remaining spots, we selected those with fluorescence ratios (representing NP-exposed samples versus unexposed samples) greater than a 1.5-fold-change cut-off, then we determined the statistical significance of the changes with a p-value ≤ 0.05 using a Student’s t-test statistical analysis on Genespring software and performing a Benjamini and Hochberg false discovery rate multiple testing correction. We thus obtained probe sets which were significantly induced or repressed after exposure to various NPs. See Additional file 4: Table S1 in the Supporting Information paragraph.
Data were analyzed through the use of IPA (Ingenuity® Systems, http://www.ingenuity.com). Canonical pathways analysis identified the pathways from the IPA library of canonical pathways that were most significant to the data set. Molecules from the dataset that met the fold change cut-off of 1.5 with p-value <0.05, and were associated with a canonical pathway in the Ingenuity Knowledge Base, were considered for the analysis. The significance of the association between the dataset and the canonical pathway was measured in two ways: 1) a ratio of the number of molecules from the dataset that map to the pathway divided by the total number of molecules that map to the canonical pathway is displayed; 2) right-tailed Fisher’s exact test was used to calculate a p-value determining the probability that the association between genes in the dataset and the canonical pathway is explained by chance alone.
Total RNA was isolated according to the manufacturer’s instructions using the RNeasy kit (Qiagen) and treated with DNase. RNA purity and concentration were determined by UV on a Nanodrop® Spectrophotometer and integrity was assessed on an Agilent 2100 Bioanalyzer (Agilent Technologies). All the samples used in this study showed a 28S/18S ratio indicating intact and pure RNA. Differential analysis of RNA from cells exposed to NPs and unexposed cells was performed by qRT-PCR with the Sybr Green PCR Master Mix (Finzyme) kit, according to the manufacturer’s instructions on Opticon II (Biorad). Primer (Sigma) sequences were, for ATP5J: 5′ GTCAGCCGTCTCAGTCCATT 3′ (forward) and 5′ AAAAGCTCCCTCTCCAGCTC 3′ (reverse); for NDUFA4: 5′ TCCAGATGTTTGTTGGGACA 3′ (forward) and 5′ GTGGAAAATTGTGCGGATGT 3′ (reverse); for NDUFS7: 5′ CGCAAGGTCTACGACCAGAT 3′(forward) and 5′ TCCCGCTTGATCTTCCTCT 3′ (reverse); for PRDX5: 5′ GTGGTGGCCTGTCTGAGTGT 3′ (forward) and 5′ ATGCCATCCTGTACCACCAT 3′ (reverse); for PRDX3: 5′ GTTGTCGCAGTCTCAGTGGA 3′ (forward) and 5′ GACGCTCAAATGCTTGATGA 3′ (reverse); for COX6A2: 5′ CTACCAACACCTCCGCATC 3′ (forward) and 5′ TCGAAGCTTCACACCTTTATTG 3′ (reverse); for SDHC: 5′TTGAGTGCAGGGGTCTCTCT 3′ (forward) and 5′ AACCAGGACAACCACTCCAG 3′ (reverse); for SDHD: 5′ GTATGCCTCTTTGCCTCTGC 3′ (forward) and 5′ GAGGCAACCCCATTAACTCA 3′ (reverse). For ATP5J, NDUFA4, NDUFS7, PRDX5, PRDX3, COX6A2 , SDHC and SDHD, the amplicon sizes were 186, 199, 241, 203, 216, 155, 240, and 203 bp, respectively. The measurements were the means of three independent experiments, and normalization was based on the total RNA mass quantified on the Nanodrop.
Availability of supporting data section
The data sets supporting the results of this article are available as additional files (Additional file 4: Table S1).
The raw data discussed in this publication have been deposited in NCBI’s Gene Expression Omnibus (GEO) repository and are accessible through GEO Series accession number GSE60128 (http://www.ncbi.nlm.nih.gov/geo/query/acc.cgi?acc=GSE60128).
Nanobyk nanoparticles degraded by light exposure
Nanobyk nanoparticles degraded by acidic treatment with SGF
Simulated gastric fluid
Trans-epithelial electric resistance
Scanning electron microscopy
Transmission electron microscopy
Fetal calf serum
Reactive oxygen species
Energy-dispersive X-ray spectroscopy
Back-scattered electron detector
Real-time quantitative polymerase chain reaction.
Cassee FR, van Balen EC, Singh C, Green D, Muijser H, Weinstein J, Dreher K: Exposure, health and ecological effects review of engineered nanoscale cerium and cerium oxide associated with its use as a fuel additive. Crit Rev Toxicol. 2011, 41 (3): 213-229.
Sehgal A, Lalatonne Y, Berret JF, Morvan M: Precipitation-Redispersion of Cerium Oxide Nanoparticles with Poly(Acrylic Acid): Towards Stable Dispersions. Langmuir. 2005, 21: 9359-9364.
Lin W, Huang YW, Zhou XD, Ma Y: Toxicity of cerium oxide nanoparticles in human lung cancer cells. Int J Toxicol. 2006, 25 (6): 451-457.
Park EJ, Choi J, Park YK, Park K: Oxidative stress induced by cerium oxide nanoparticles in cultured BEAS-2B cells. Toxicology. 2008, 245 (1–2): 90-100.
Auffan M, Rose J, Wiesner MR, Bottero JY: Chemical stability of metallic nanoparticles: a parameter controlling their potential cellular toxicity in vitro. Environ Pollut. 2009, 157 (4): 1127-1133.
Xia T, Kovochich M, Liong M, Madler L, Gilbert B, Shi H, Yeh JI, Zink JI, Nel AE: Comparison of the mechanism of toxicity of zinc oxide and cerium oxide nanoparticles based on dissolution and oxidative stress properties. ACS Nano. 2008, 2 (10): 2121-2134.
Schubert D, Dargusch R, Raitano J, Chan SW: Cerium and yttrium oxide nanoparticles are neuroprotective. Biochem Biophys Res Commun. 2006, 342 (1): 86-91.
Gaiser BK, Fernandes TF, Jepson MA, Lead JR, Tyler CR, Baalousha M, Biswas A, Britton GJ, Cole PA, Johnston BD, Ju-Nam Y, Rosenkranz P, Scown TM, Stone V: Interspecies comparisons on the uptake and toxicity of silver and cerium dioxide nanoparticles. Environ Toxicol Chem. 2012, 31 (1): 144-154.
Wang L, Nagesha DK, Selvarasah S, Dokmeci MR, Carrier RL: Toxicity of CdSe Nanoparticles in Caco-2 Cell Cultures. J Nanobiotechnol. 2008, 6: 11-
Prabhakaran KSR, Kumbhar CS, Melkeri A, Gokhale NM, Sharma SC: Heterocoagulation moulding of alumina powder suspensions prepared using citrate dispersant. Ceram Int. 2010, 36 (1): 1-8.
Yin L, Wang Y, Pang G, Koltypin Y, Gedanken A: Sonochemical synthesis of cerium oxide nanoparticles, effect of additives and quantum size effect. J Colloid Interface Sci. 2002, 246 (1): 78-84.
Zeyons O, Thill A, Chauvat F, Menguy N, Cassier-Chauvat C, Oréar C, Daraspe J, Auffan M, Rose J, Spalla O: Direct and indirect CeO2 nanoparticles toxicity for Escherichia coli and Synechocystis. J Nanotoxicol. 2009, 3 (4): 284-295.
Peterson MD, Bement WM, Mooseker MS: An in vitro model for the analysis of intestinal brush border assembly. II. Changes in expression and localization of brush border proteins during cell contact-induced brush border assembly in Caco-2BBe cells. J Cell Sci. 1993, 105 (Pt 2): 461-472.
Peterson MD, Mooseker MS: An in vitro model for the analysis of intestinal brush border assembly. I. Ultrastructural analysis of cell contact-induced brush border assembly in Caco-2BBe cells. J Cell Sci. 1993, 105 (Pt 2): 445-460.
Worle-Knirsch JM, Pulskamp K, Krug HF: Oops they did it again! Carbon nanotubes hoax scientists in viability assays. Nano Lett. 2006, 6 (6): 1261-1268.
Fisichella M, Dabboue H, Bhattacharyya S, Saboungi ML, Salvetat JP, Hevor T, Guerin M: Mesoporous silica nanoparticles enhance MTT formazan exocytosis in HeLa cells and astrocytes. Toxicol Vitro. 2009, 23 (4): 697-703.
Briede JJ, van Delft JM, de Kok TM, van Herwijnen MH, Maas LM, Gottschalk RW, Kleinjans JC: Global gene expression analysis reveals differences in cellular responses to hydroxyl- and superoxide anion radical-induced oxidative stress in caco-2 cells. Toxicol Sci. 2010, 114 (2): 193-203.
Limbach LK, Li Y, Grass RN, Brunner TJ, Hintermann MA, Muller M, Gunther D, Stark WJ: Oxide nanoparticle uptake in human lung fibroblasts: effects of particle size, agglomeration, and diffusion at low concentrations. Environ Sci Technol. 2005, 39 (23): 9370-9376.
Eom HJ, Choi J: Oxidative stress of CeO2 nanoparticles via p38-Nrf-2 signaling pathway in human bronchial epithelial cell, Beas-2B. Toxicol Lett. 2009, 187 (2): 77-83.
Martell AE, Smith RM: Critical Stability Constants, Other Organic Ligands. Volume 3, 4th edition. 1977, New York and London: Plenum Press, 158-
Diot M-A: Aging and alteration of manufactured nanocomposites. PhD Thesis in Environmental Geosciences. 2012, France: Université Paul Cézanne-Aix Marseille III
Cedervall T, Lynch I, Lindman S, Berggard T, Thulin E, Nilsson H, Dawson KA, Linse S: Understanding the nanoparticle-protein corona using methods to quantify exchange rates and affinities of proteins for nanoparticles. Proc Natl Acad Sci U S A. 2007, 104 (7): 2050-2055.
Liu W, Rose J, Plantevin S, Auffan M, Bottero JY, Vidaud C: Protein corona formation for nanomaterials and proteins of a similar size: hard or soft corona?. Nanoscale. 2013, 5 (4): 1658-1668.
Pelletier DA, Suresh AK, Holton GA, McKeown CK, Wang W, Gu B, Mortensen NP, Allison DP, Joy DC, Allison MR, Brown SD, Phelps TJ, Doktycz MJ: Effects of engineered cerium oxide nanoparticles on bacterial growth and viability. Appl Environ Microbiol. 2010, 76 (24): 7981-7989.
Horie M, Kato H, Fujita K, Endoh S, Iwahashi H: In vitro evaluation of cellular response induced by manufactured nanoparticles. Chem Res Toxicol. 2012, 25 (3): 605-619.
Lee TL, Raitano JM, Rennert OM, Chan SW, Chan WY: Accessing the genomic effects of naked nanoceria in murine neuronal cells. Nanomedicine. 2012, 8 (5): 599-608.
Lee TL, Chan WY, Rennert OM, Lee TL, Chan WY, Rennert OM: Assessing the safety of nanomaterials by genomic approach could be another alternative. ACS Nano. 2009, 3 (12): 3830-author reply 3830–3831
Fisichella M, Berenguer F, Steinmetz G, Auffan M, Rose J, Prat O: Intestinal toxicity evaluation of TiO2 degraded surface-treated nanoparticles: a combined physico-chemical and toxicogenomics approach in caco-2 cells. Part Fibre Toxicol. 2012, 9 (1): 18-
Prat O, Berenguer F, Steinmetz G, Ruat S, Sage N, Quemeneur E: Alterations in gene expression in cultured human cells after acute exposure to uranium salt: Involvement of a mineralization regulator. Toxicol In Vitro. 2010, 24: 160-168.
Benameur L: Genotoxicity of manufactured cerium oxide nanoparticles and role of oxidative stress. PhD Thesis in Environmental GeosciencesUniversité de la Méditerranée. 2011, France: Aix-Marseille II
Rosenkranz P, Fernandez-Cruz ML, Conde E, Ramirez-Fernandez MB, Flores JC, Fernandez M, Navas JM: Effects of cerium oxide nanoparticles to fish and mammalian cell lines: An assessment of cytotoxicity and methodology. Toxicol In Vitro. 2012, 26 (6): 888-896.
Dowding JM, Dosani T, Kumar A, Seal S, Self WT: Cerium oxide nanoparticles scavenge nitric oxide radical ( NO). Chem Commun (Camb). 2012, 48 (40): 4896-4898.
Di Cicco AA, Minicucci M, Principi E, Novello N, Cognigni A, Olivi L: Novel xafs capabilities at elettra synchrotron light source. Journal of Physics: Conference Series 2009. 2009
Newville M: IFEFFIT: interactive XAFS analysis and FEFF fitting. J Synchrotron Radiat. 2001, 8 (Pt 2): 322-324.
Ludwig S, Tinwell H, Schorsch F, Cavaille C, Pallardy M, Rouquie D, Bars R: A molecular and phenotypic integrative approach to identify a no-effect dose level for antiandrogen-induced testicular toxicity. Toxicol Sci. 2011, 122 (1): 52-63.
The authors wish to thank the Agence Nationale de la Recherche for funding the AgingNano&Troph project (ANR-08-CESA-001). Technical help for SEM studies was provided by C. Dominici, CP2M platform, Université Aix-Marseille. We also thank J. Courageot, Université Aix-Marseille for fruitful discussions.
The authors declare that they have no competing interests.
MF carried out the cell culture, viability studies, size determination, and cellular SEM studies, participated in the microarray experiments and drafted the manuscript. GS performed RNA extraction, labelling and microarray experiments. FB carried out the statistical analyses and bioinformatics studies. MA performed the physicochemical characterization of NPs including TEM and XANES. JR coordinated the different teams taking part in the whole project and provided the NPs. OP conceived the study, participated in design and experiments, coordinated the team and wrote the final manuscript. All authors read and approved the final manuscript.
Electronic supplementary material
Additional file 1: Figure S1: Experimental XANES spectra at the Ce L3-edge of CeO2 NPs, the unaltered Nanobyk™, light-degraded Nanobyk (Nanobyk DL) and acid-degraded Nanobyk (Nanobyk DA), nano-sized CeO2, and micron-sized CeO2. No change in the cerium redox state was observed between initial and altered Nanobyk. (TIFF 4 MB)
Additional file 2: Figure S2: SEM image of Caco-2 cells exposed for 72 h to 170 μg/mL NPs. Caco-2 cells were grown on bicameral wells (PET, pores 1 μm) and differentiated for 21 days. The cells were exposed to NPs (170 μg/mL). After 72 h incubation, the cells were washed, fixed and dehydrated. They were observed by SEM. Top lane) Magnification 2,000 x. Bottom lane) Magnification 16,000 x. Clear spot deposits are visible at the cell surface only for light-degraded Nanobyk. (TIFF 5 MB)
Additional file 3: Figure S3: Microarray scatter plots. Caco-2 cells were cultured and differentiated for 21 days. They were exposed for 72 h to 21.25 μg/mL CeO2 NPs. The scatter plots represent the raw fluorescence intensities of genes filtered at the threshold intensity signal after hybridization (n = 4). From Blue to Red: increasing fluorescence intensity. The number of genes detected above the signal threshold was compared for each type of NP (y-axis) versus their own control (x-axis). A) Unexposed cells versus unexposed cells (control 2 versus control 1) as negative control. B) H2O2-exposed cells versus unexposed cells (control 3) as positive control. C) Pristine (surface-untreated) cerium-oxide-NP-exposed cells versus unexposed cells (control 3). D) NB-exposed cells versus unexposed cells (control 1). E) NB-DL-exposed cells versus unexposed cells (control 1). F) NB-DA-exposed cells versus unexposed cells (control 2). These graphs do not display the significantly altered genes since they represent the raw fluorescence signals before applying statistical tests. Nevertheless, they give a good, rough overview of the amplitude alterations caused by the different nanoparticles. (TIFF 907 KB)
Additional file 4: Table S1: Complete lists of significant, differentially expressed genes including fold change and p-value in each probe set. NA means no available information. (XLS 2 MB)
Authors’ original submitted files for images
About this article
Cite this article
Fisichella, M., Berenguer, F., Steinmetz, G. et al. Toxicity evaluation of manufactured CeO2 nanoparticles before and after alteration: combined physicochemical and whole-genome expression analysis in Caco-2 cells. BMC Genomics 15, 700 (2014). https://doi.org/10.1186/1471-2164-15-700