- Open Access
Quantification and visualization of cellular uptake of TiO2 and Ag nanoparticles: comparison of different ICP-MS techniques
Journal of Nanobiotechnology volume 14, Article number: 50 (2016)
Safety assessment of nanoparticles (NPs) requires techniques that are suitable to quantify tissue and cellular uptake of NPs. The most commonly applied techniques for this purpose are based on inductively coupled plasma mass spectrometry (ICP-MS). Here we apply and compare three different ICP-MS methods to investigate the cellular uptake of TiO2 (diameter 7 or 20 nm, respectively) and Ag (diameter 50 or 75 nm, respectively) NPs into differentiated mouse neuroblastoma cells (Neuro-2a cells). Cells were incubated with different amounts of the NPs. Thereafter they were either directly analyzed by laser ablation ICP-MS (LA-ICP-MS) or were lysed and lysates were analyzed by ICP-MS and by single particle ICP-MS (SP-ICP-MS).
All techniques confirmed that smaller particles were taken up to a higher extent when values were converted in an NP number-based dose metric. In contrast to ICP-MS and LA-ICP-MS, this measure is already directly provided through SP-ICP-MS. Analysis of NP size distribution in cell lysates by SP-ICP-MS indicates the formation of NP agglomerates inside cells. LA-ICP-MS imaging shows that some of the 75 nm Ag NPs seemed to be adsorbed onto the cell membranes and were not penetrating into the cells, while most of the 50 nm Ag NPs were internalized. LA-ICP-MS confirms high cell-to-cell variability for NP uptake.
Based on our data we propose to combine different ICP-MS techniques in order to reliably determine the average NP mass and number concentrations, NP sizes and size distribution patterns as well as cell-to-cell variations in NP uptake and intracellular localization.
Due to their enhanced optical, electronical and antimicrobial properties, nanoparticles (NPs) are used in a variety of different consumer products like cosmetics, textiles or packaging and also in nanomedicine or electronics . Titanium dioxide nanoparticles (TiO2 NPs) and silver nanoparticles (Ag NPs) belong to the group of highly commercialized NPs [2–5]. TiO2 NPs are frequently used as UV filters in cosmetics due to their absorption and scattering properties. However, TiO2 E171 is also used as a food additive, with a fraction of E171 being nanoscaled. Some types of TiO2 materials, in dependence on their crystal structure and chemical surface coating, have photocatalytic properties and are therefore used in sensors and self-cleaning surfaces [6, 7]. Ag NPs are often used because of their antimicrobial properties, e.g. in textiles but also for several medical applications such as wound dressings [8, 9]. Thus, human exposure to these kinds of NPs is increasing. Numerous in vivo and in vitro studies have evaluated the toxicity and toxic mechanisms of these NPs, which is summarized in several review articles [10, 11].
However, for safety assessment it is also important to analyze and quantify cellular uptake. Electron microscopy-based methods such as scanning electron microscopy (SEM) or transmission electron microscopy (TEM) can be used to localize NPs in intracellular ultrastructures with high spatial resolution. In combination with energy-dispersive X-ray spectroscopy (EDX) they also allow to identify the materials [12–14]. However, these techniques require extensive, time-consuming sample preparation and typically provide qualitative information . Quantification might be also possible but requires time-consuming 3-D reconstruction and automated image analysis.
In cell biology, flow cytometry and/or fluorescent microscopy are often used for quantification of cellular uptake. In principle, both techniques are also applicable for fluorescent-labelled NPs [16, 17]. These techniques are easy to use and also allow for time resolved analysis. Possible drawbacks are dye leakage or possible surface modification due to dye-labelling, both of which may strongly influence the results and hence need to be considered beforehand . An absolute quantification is not possible via these approaches.
Inductively coupled plasma mass spectrometry (ICP-MS) is a common technique for absolute quantification of the cellular uptake of metal or metal oxide NPs. It offers high sensitivity and selectivity for elemental analysis [19, 20]. Routinely it requires that cells are lysed before analysis. The absolute uptake per cell may be calculated after the measurement taking into account the cell number of the sample. However, this procedure reveals an average number only. In addition this approach will yield the total amount of the particular metal only. It will not allow to differentiate between single particles and agglomerated or ionic species. Also, it will not give information about the sizes of NPs. Despite these drawbacks ICP-MS is an established approach to quantify NP uptake and has been used in many studies. For instance it has been repeatedly found that the cellular uptake depends on the sizes of NPs [21, 22]. Mostly these studies present only calculated number concentrations and average amounts. Due to these limitations, little is known about real numbers of NPs per cell or about cell-to-cell heterogeneity. In the meantime, several modifications of ICP-MS became available that allow for single cell or single particle analysis [e.g. single cell ICP-MS (SC-ICP-MS) and single particle ICP-MS (SP-ICP-MS)] [14, 23, 24]. In SP-ICP-MS, highly diluted samples are measured. Since each signal in SP-ICP-MS corresponds to a single particle, the frequency of ICP-MS signals can be used to estimate the NP number concentration. On the other side, the intensity of signals is related to the amount of the chemical element and thus to the sizes of the respective NPs. When assuming spherical particle shapes, NP sizes and size distributions can be derived using SP-ICP-MS. For instance, the uptake of gold NPs in human umbilical vein-derived endothelial cells (HUVECs) was analyzed by SP-ICP-MS and a concentration-dependent increase in uptake was detected without agglomeration . ICP-MS can be also coupled to laser ablation (LA-ICP-MS), which then allows the analysis of solid materials. This method has been applied to quantify gold, silver and aluminum oxide NPs at the single cell level [25–27]. The high spatial resolution of the LA-ICP-MS images also allows for sub-cellular localization of NPs or for detection of NP aggregation in cells .
The work flow of our study is depicted in Fig. 1. The aim of the present study was to apply and to compare conventional ICP-MS, SP-ICP-MS, and LA-ICP-MS in the quantification of the cellular uptake of two types of TiO2 NPs (diameter of 7 and 20 nm, as determined by X-ray, respectively) and two types of Ag NPs (diameter of 50 and 70 nm, as determined by TEM, respectively). While the average NP mass concentration was determined by ICP-MS, average NP number concentration and size distribution was available from SP-ICP-MS. Cell-to-cell heterogeneity of NP uptake and intracellular distribution was analyzed by LA-ICP-MS. A differentiated Neuro-2a mouse neuroblastoma cell has been chosen because several studies indicated that NPs might be taken up into the central nervous system thereby exerting neurotoxic effects [29–32].
Results and discussion
Characterization of NPs
We used two sizes of TiO2 NPs with diameters of 7 nm and 20 nm (as determined by X-ray), respectively. NP sizes were also analyzed by TEM (Fig. 2a, b). Their average hydrodynamic diameters in pure water was determined by dynamic light scattering (DLS). Size distribution in complete cell culture medium (CCM) containing serum was assessed by DLS (Fig. 2e) and nanoparticle tracking analysis (NTA) (Additional file 1: Figure S1). Data indicate some agglomeration for both types of TiO2 NPs but dispersion quality was still reasonably good. The alkali modification process for TiO2 NPs increases the density of surface hydroxyl groups and enhances their dispersion . Furthermore, we used two sizes of Ag NPs with TEM diameters of 50 and 75 nm, respectively (Fig. 2c, d). Sizes determined by TEM was reported by the manufacturer. In addition, DLS was used to assess the average hydrodynamic diameter in pure water. Size distribution in CCM was investigated by DLS (Fig. 2f) and NTA (Additional file 1: Figure S1). Ag NPs were very well dispersed with only little sign of agglomeration visible using NTA. Material characterization is summarized in Table 1.
Assessment of NP-mediated cytotoxicity
Prior to the cellular uptake experiments, we carefully analyzed the cytotoxicity of the TiO2 and Ag NPs after 24 h of incubation (Additional file 1: Figure S2). The results show that both sizes of TiO2 NPs display no toxicity up to 25 µg/mL. Conversely, both sizes of Ag NPs showed a minimal toxicity at 25 µg/mL, with cell viabilities of 87 % for 50 nm and 90 % for 75 nm Ag NPs. According to these results, we used clearly non-cytotoxic doses in all subsequent experiments (i.e. 2 and 10 µg/mL of both Ag NPs and TiO2 NPs).
Cellular uptake of NPs depends on particle size and concentration
We first performed calibrations using Ti and Ag ionic standards and In ions as internal standard. These resulted in linear correlations with squared correlation coefficients of (R2) >0.995 for both, Ti and Ag. The limit of detection (LOD) (as 3× STD+ background, n = 3) was determined at 0.05 pg Ag/cell and 0.31 pg TiO2/cell, respectively.
Using these calibrations, we quantified the cellular uptake by measuring the total amounts of Ti and Ag after digestion of Neuro-2a cells upon treatment with two concentrations, i.e. 2 and 10 μg/mL (Fig. 3a, b).
Higher mass amounts of TiO2 and Ag were taken up after incubation with larger particles compared to the smaller ones. Furthermore, uptake was increased at higher concentrations. For the TiO2 NPs this resulted in a 1.9 and 2.6-fold higher cellular Ti amount for the 7 and 20 nm NPs at 10 µg/mL when compared to 2 µg/mL, respectively (Fig. 3a). In the case of Ag NPs only the 75 nm (TEM) showed a clear increase in uptake after treatment with the higher incubation concentration (2.9-fold) (Fig. 3b). To rule out the possibility that the detected signals were due to NPs that physically attached to the surface of the cell cultures plates, we performed control treatments without any cells, which were analyzed accordingly (Fig. 3a, b). After identical sample preparation in the controls almost no Ag could be detected (Fig. 3b). However, some Ti was detected, which is likely to represent the fraction of NPs that unspecifically attached to the cell culture plates and which could not be completely removed by washing (Fig. 3a). In the case of 10 µg/mL of 7 nm TiO2 NPs (X-ray), the numbers were 109 ng total Ti in the presence of cells (equals 0.36 pg/cell) versus 46 ng in the absence of cells (equals 0.19 pg/cell when assuming the same cell number as in the treatment group). Similarly, for 10 µg/mL of 20 nm TiO2 NPs (X-ray) 559 ng of Ti was detected when cells were present (equals 1.93 pg/cell), whereas 443 ng were detected in controls (equals 1.53 pg/cell).
Furthermore, we used SP-ICP-MS to quantify the NP numbers in Neuro-2a cells directly, which was, according to our knowledge, investigated here for the first time. First, we performed a calibration experiment by using NP suspensions. The LODsize and LODnumberNP of Ag NPs was 22 nm and 2.26 × 105 particles, respectively. The LODsize and LODnumberNP of TiO2 NPs was 69 nm and 1.92 × 105 particles, respectively. Therefore, the 7 nm TiO2 NPs with a secondary size of 48 nm (DLS) could not be detected. However, the 20 nm TiO2 NPs (X-ray) as well as both types of Ag NPs could be quantified via SP-ICP-MS. The 20 nm TiO2 NPs (X-ray) showed a concentration-dependent uptake into Neuro-2a cells as indicated by the SP-ICP-MS measurements (Fig. 4a). In addition to the concentration dependency, for Ag NPs we were able to confirm a size dependency as well, as the number of NPs per cell increased with decreasing particle size (Fig. 4b). Therefore, the smaller Ag particles can penetrate into cells more efficiently.
Assuming ideal spheres and no dissolution for both types of NPs, the NP numbers per cell can also be calculated using the results from ICP-MS. These results confirmed that the treatment with the smaller TiO2 and Ag NPs resulted in higher particle numbers per cell (Fig. 4a, b). However, assuming the TEM size as single particle diameter, the particle numbers calculated based on ICP-MS data were considerably higher when compared to the particle numbers directly measured by SP-ICP-MS using the same lysates. Between calculated and measured NP numbers the differences were 100-fold for TiO2 and twofold for Ag NPs (Fig. 4a, b). By contrast, assuming DLS size as single particle diameter, the differences between calculated and measured NP numbers decreased to about three- to fourfold for TiO2 and 1.1- to 1.4-fold for Ag NPs. This result indicated that NP sizes determined by DLS were more suitable for the transformation of NP amounts into NP numbers, when compared to NP sizes determined via TEM or X-ray. Indeed, the differences between estimated and measured NP numbers may be explained, at least partially, by NP agglomeration in cells, which was found higher in the case of TiO2 NPs. This aspect will be discussed in the following section in more detail.
LA-ICP-MS also confirms the size-dependent cellular uptake of NPs
For NP quantification by LA-ICP-MS we first analyzed the calibration curve, which was based on adding NPs to a cell lysate of untreated cells (Additional file 1: Figure S3a). A laser spot size of 250 μm (line distance of 240 μm) and a scan speed of 200 μm/s were considered to be optimal LA parameters. For silver, the calibration range comprised five Ag-containing spots and one control spot without Ag. The latter was pipetted at around X = 2.5 mm but could not be distinguished from the background of the glass slide. A background correction for each drop was performed. Since the upper and lower area showed a different background signal, both replicates were corrected separately. A good correlation (R2 = 0.995) between the amount of silver and the integrated signal intensity was observed and a limit of detection of 78.5 pg was calculated (Additional file 1: Figure S3b).
LA-ICP-MS in general is able to provide high spatial localization information (1 μm pixel size in x-direction and 6 μm in y-direction) as reported before by Drescher and co-workers analyzing Au and Ag NP aggregates in the mouse fibroblast 3T3 cell line . A laser spot size of 4 μm (line distance of 6 μm) and a scan speed of 5 μm/s was used. As Neuro-2a cells were smaller compared to 3T3 cells this may result in a much lower number of pixels to represent the NPs in a single cell but does not affect the integrated sensitivity under the same conditions. Therefore, for Neuro-2a cells a reasonable sub-cellular localization requires further optimization of the ablation parameters. However, by decreasing the line distance to 5 μm (1 μm pixel size in x-direction and 5 μm in y-direction in spatial resolution) we could show that no NPs were localized in the cell neurites. Neurites propagate the signals between neural cells and are usually not responsible for uptake. However, we may not entirely exclude that NP concentrations in neurites were below the detection limits of LA-ICP-MS.
The contour plots for the 107Ag signal intensities of the dried cells nicely corresponded with bright field images of Neuro-2a cells before ablation (compare Fig. 5a, b). We found that cells after incubation with 75 nm Ag NPs (TEM) often revealed more 107Ag spots with a higher intensity compared to cells treated with 50 nm Ag NPs (TEM). Furthermore, 75 nm Ag NPs (TEM) could frequently be detected outside the cells while 50 nm Ag NPs (TEM) were mainly detected within the cell areas only.
Signals from 99 and 109 cells from several ablated areas were integrated after treatment with 50 and 75 nm Ag NPs (both TEM sizes), respectively. Using the calibration curve, the calculated amounts of silver per cell after a 2 µg/mL incubation ranged from 0.006 to 0.528 ng for 50 nm Ag NPs (0.081 ± 0.067 ng in average), and from 0.001 to 1.332 ng for 75 nm Ag NPs (0.205 ± 0.188 ng in average), respectively (Fig. 5c). This again confirmed a higher NP mass per cell for the bigger 75 nm particles and at the same time demonstrates a high cell-to-cell variability, which seems increasing at higher treatment concentrations.
Assuming ideal spheres, DLS size as particle diameter, consisting purely of silver for both nanoparticles types, the total silver amounts per cell were converted into NP numbers (Fig. 5d). Again, a higher NP number per cell was found after incubation of the cells with the smaller 50 nm Ag NPs (TEM) (see Table 2).
Using the same strategy as for the Ag NPs, we could not achieve an according calibration for the TiO2 NPs though. The 48Ti signal spots for the pipetted calibration spots could not be detected and integrated clearly. Instead the spot areas showed a depleted signal intensity compared to a relatively high and irregular background (data not shown). Higher spots within these areas might indicate some flow mechanism for the TiO2 NPs similar to the coffee stain effect [34, 35]. As our calibration was not successful, we can only provide 48Ti signal intensities in this study but no quantification. For further studies one may consider to use aqueous Ti standards instead of TiO2 NPs.
Figure 6a–d show exemplarily the overlaps of the contour plots for the 48Ti signals with the corresponding bright field images of the dried Neuro-2a cells. In agreement with prior results, more 48Ti signal spots in each cell were observed after higher concentrated incubations (10 µg/mL) compared to lower concentrations (2 µg/mL). Similarly, more 48Ti signal spots could be detected for larger TiO2 NPs (20 nm, X-ray). Part of the titanium signal detected using conventional ICP-MS may stem from particles that unspecifically attached to the surface of the cell culture plate, which is causing an overestimation of cellular uptake. Using LA-ICP-MS allows to selectively integrate only signals within the cells thereby correcting any background and eliminating this error.
Integration of the dried cells showed that after incubation with a higher NP concentration or larger NPs, a higher signal intensity of 48Ti can in average be found per cell which equals a higher amount (Fig. 6e). The 10 µg/mL incubation resulted for both NP sizes in an approximately 4.5-fold increased signal intensity. The larger 20 nm TiO2 NPs led to twice the signal intensity, independent of the used NP concentration (Fig. 6e).
Despite the fact that calibration failed for the TiO2 NPs, we could use our data to obtain the relative numbers of particles per cell. Utilizing the DLS size ratio between both TiO2 NP types, the integrated signals of 48Ti per cell were converted to relative NP numbers—only missing the calibration factor (cps/ng)—and could be compared. Figure 6f shows the distribution of the relative numbers of particles per cell for each exposure condition. On average, the relative number of the smaller TiO2 NPs per cell was found to be four times the number of the larger TiO2 NPs (Table 2; Fig. 7). This again confirms that smaller particles are more easily incorporated into cells. At the same time a big variance in the numbers of NPs per cell was seen especially after incubation with the higher concentration (10 µg/mL). This indicates a cell-to-cell diversity, which may be even increased at higher treatment concentrations.
Using LA-ICP-MS we could detect even the smaller TiO2 NPs with a diameter of 7 nm (X-ray) above background levels, which was not the case in the corresponding SP-ICP-MS experiments.
NP agglomerates in cells can be detected using SP-ICP-MS
In addition to particle numbers, SP-ICP-MS can also be applied to estimate NP size distributions. A cell-free 20 nm TiO2 NP suspension in ultrapure water revealed an average diameter of 115 nm and a size range of 76–260 nm (Additional file 1: Figure S4a, b). This size value was close to the size value determined by DLS (130 nm). However, in cell lysates the average NP size value increased to 134 nm with size ranging from 76 to 300 nm, especially for the 10 µg/mL incubation (Additional file 1: Figure S5a, b). Cell-free 50 and 75 nm Ag NP suspensions (both TEM sizes) in pure water showed 46 and 72 nm in average diameter, respectively (Additional file 1: Figure S4c–f). Again, in cell lysates, average sizes of both Ag NPs also increased to 55 and 84 nm at 10 µg/mL because more particles could be detected in the range of 150–200 nm (Additional file 1: Figure S5c-f). This indicates that NP agglomerates are being formed in Neuro-2a cells after particle uptake. Such agglomerates of NPs, ranging from submicron to micron size, can frequently be found in cells by different electron microscope techniques like TEM [36, 37]. These data correspond well with lower numbers of NPs measured by SP-ICP-MS as theoretically calculated based on conventional ICP-MS data. One reason for this discrepancy is likely the agglomeration of both NP types. Agglomeration is more pronounced for TiO2, which nicely conforms with the higher difference between calculated and measured NP numbers for TiO2 NPs. In addition, Ag NPs could dissolve into silver ions. We observed a higher background noise for cell samples treated with Ag NPs compared to control cells in pure water (data not shown), which may be due to Ag NP dissolution. Finally, for TiO2 the LODsize hinders the detection of small TiO2 particles by SP-ICP-MS and may thereby also affect the results.
Studies applying conventional ICP-MS have already found a size-dependent uptake of TiO2 and Ag NPs in mammalian cells [38, 39]. However, in these studies frequently smaller NPs were reported to show a higher mass concentration in cells, which is in contrast to the results in our study. Zhu et al. analyzed uptake of silica NP by atomic absorption spectrometry (AAS) in HeLa cells, and found a higher uptake efficiency for smaller SiO2 NPs in both mass and estimated number concentrations . Furthermore, some studies reported no size-dependency of the uptake, as shown for citrate-coated Ag NPs and human lung cells analyzed by AAS . These studies rely on indirect, average results. Our study clearly showed a size-dependent uptake for both Ag and TiO2 NPs in Neuro-2a cells. However, we find a higher mass concentration for the larger particles but a higher particle number for the smaller NPs, consistently across different techniques. The different results between all these studies may also be caused by different uptake mechanisms of NPs in different cell types. Furthermore, differences may arise from different surface modifications. Therefore a general conclusion might not be possible at the moment until the underlying mechanisms of cellular uptake are fully understood. The main features of each technique applied in our study is summarized in Table 3.
In the present study, ICP-MS, SP-ICP-MS, and LA-ICP-MS were used to quantify the uptake of TiO2 NPs or Ag NPs in neuroblastoma cells. While cellular uptake was clearly NP size-dependent, we consistently found a higher mass concentration in the case of the larger NPs but a higher particle number for the smaller NPs. ICP-MS provides average mass quantification data, which can be converted into NP numbers. The results may, however, be confounded by NP agglomeration inside cells, resulting in an overestimation of NP numbers. Furthermore, NPs may unspecifically attach to the surface of the cell culture dishes and withstand the regular washing steps prior to analysis. This again would lead to an overestimation of the NP amounts in conventional ICP-MS. In particular this was observed for the cellular uptake of TiO2 NPs in our study. SP-ICP-MS directly measures NP numbers. Furthermore, using SP-ICP-MS it is possible to estimate size distributions of spherical particles directly in cell lysates. This allows to analyze possible NP agglomeration inside cells. However, smaller TiO2 particles cannot be measured due to the high LODsize value. By LA-ICP-MS it becomes possible to directly quantify NP mass concentrations at single cell level as done here for Ag NPs. On the other side, we observed difficulties in the calibration of TiO2 NPs, so that we only could derive relative signal intensities. Notwithstanding applying LA-ICP-MS it is possible to obtain information on the sub-cellular localization of particles. As each technique offers specific advantages we propose to combine them in order to successfully elucidate different aspects of NP’s cellular uptake.
Ultrapure water (18.2 MΩ/cm) was generated by a Milli-Q Plus system from Merck Millipore (Darmstadt, Germany). The Ag elemental standard as well as nitric acid (p. A., 65 %) were purchased from Merck (Darmstadt, Germany). The Ti and In elemental standard were purchased from Sigma-Aldrich (TraceCERT®, Steinheim, Germany). Hydrogen peroxide (H2O2) solution (p.A., 30 %), sodium hydroxide (NaOH), Triton X-100 solution, forskolin, 3-isobutyl-1-methylxanthine (IBMX), and paraformaldehyde were purchased from Sigma-Aldrich (Steinheim, Germany). Hydrochloric acid (p.A., 37 %) was bought from Applichem (Darmstadt, Germany). Hydrofluoric acid (p.A., 5 %) was bought from Carl Roth (Karlsruhe, Germany). SuperFrost®Plus Slides were used as glass slides for cell culture LA-ICP-MS experiments (Thermo Fisher Scientific GmbH, Dreieich, Germany).
Commercially available 50 and 75 nm Ag nanospheres, carrying a citrate modification, were utilized (NanoComposix, Prague, Czech Republic). Alkali-modified TiO2 NPs were synthesized as described in a previous study . Briefly, 1 g TiO2 commercial nanopowder (ST-01, 7 nm or ST-21, 20 nm, 100 % anatase, Ishihara Corporation, Japan) was dispersed in a 100 mM H2O2 and 8 M NaOH mixed aqueous solution. Then, the suspension was heated to 50 °C and kept for 24 h. After centrifugation at 8000 rpm for 20 min, the particles were washed twice with de-ionized water and re-dispersed in a 1.6 M HNO3 solution. The suspension was stirred for 3 h and then centrifuged at 13,500 rpm for 20 min. After three times wash with de-ionized water, the TiO2 NPs were dried at 60 °C and re-dispersed in water for subsequent experiments. Final concentrations of the suspension were determined by inductively coupled plasma optical emission spectrometry (ICP-OES) (Agilent 725, Santa Clara, USA). Stock solutions of Ag NPs and TiO2 NPs were first ultrasonicated for 5 min and then diluted to 100 μg/mL in the indicated medium. All NP suspensions were freshly prepared before each experiment.
Characterization of nanoparticles
The particle size and morphology of the alkali-modified TiO2 NPs in suspension were analyzed using a JEM2100 transmission electron microscope at an acceleration voltage of 200 kV (TEM) (JEOL, Japan). The hydrodynamic size of the Ag NPs and TiO2 NPs in stock solution and cell culture medium (CCM) were monitored using a Zetasizer Nano ZS apparatus (Malvern Instruments GmbH, Herrenberg, Germany). Particle solutions were diluted for the DLS measurement to a final concentration of 100 μg/mL for TiO2 NPs and 10 μg/mL for Ag NPs. For nanoparticle tracking analysis (NTA) we used a NanoSight LM20 system (Malvern, Germany) equipped with a green laser (532 nm) at RT (22 °C). Sizes were calculated from videos (60 s, 30 frames per s) by NTA3.1 software. Fetal calf serum (FCS) contained numerous agglomerates, which disturbed analysis. Therefore, NP dispersions were prepared in CCM with final concentrations of 10 μg/ml for nanosilver and 100 μg/ml for TiO2 and then diluted 1:40 into protein-free MEM such that the serum-agglomerates were not detectable any more. Proteincorona of NPs were considered as rather stable, not likely to disintegrate during the time period of NTA measurements. Nanosilver dissolution in water was determined using ICP-MS as described below. Two different concentrations were tested, i.e. 2 and 10 μg/ml. Suspensions were incubated for 24 h at 37 °C and were then centrifuged at a table top centrifuge at 16,000×g for 30 min to remove NPs. Supernatants were filtered through Amicons filters (cut off 30 kDa) and then processed as described below for ICP-MS analysis.
Mouse neuroblastoma (Neuro-2a) cells (Cell Lines Service GmbH, Eppelheim, Germany) were cultured in MEM medium (Gibco, Darmstadt, Germany) supplemented with 10 % fetal calf serum (FCS) (Pan Biotech, Aidenbach, Germany), 2 mM l-glutamine, 0.1 mM non-essential amino acids, and 1.0 mM sodium pyruvate (Gibco, Darmstadt, Germany). Cells were cultivated at 37 °C, 5 % CO2 and 95 % relative humidity. Twenty four hours after seeding, cells were differentiated using 30 μM forskolin and 200 μM 3-isobutyl-1-methylxanthine (IBMX) (both obtained from Sigma-Aldrich, Steinheim, Germany) in MEM/1 % FCS medium for 2 days into neuronal-like cells.
WST-1 cell viability assay was used to evaluate the toxicity of TiO2 NPs and Ag NPs according to manufacturer’s instructions (Roche Diagnostics, Mannheim, Germany). Neurite-bearing cells (1.8 × 104 cells/cm2) were treated with 5, 10 and 25 μg/mL TiO2 NPs or Ag NPs, respectively, in 96-well plates for 24 h. Interfering NPs were removed in a table top centrifuge by centrifugation with maximum speed prior to spectrophotometric read-out (TECAN, Crailsheim, Germany) at 450 nm.
Cell incubation and sample preparation
For analysis by ICP-MS and SP-ICP-MS, cells were seeded and differentiated in 12-well plates (1.8 × 104 cells/cm2). They were exposed to 2 or 10 μg/mL NPs in MEM/5 % FCS medium for 24 h. It should be noted, that in vitro test concentrations in the range from 1 to 10 µg/cm2 correlate very well to test concentrations usually used in in vivo inhalation studies and in particular they correlate well to the overload dose, i.e. the dose where toxic effects become detectable. Therefore, in vitro test concentrations in the range from 1 to 10 µg/cm2 are useful for comparing the data later on to results obtained in in vivo experiments.
Before analysis cells were washed three times with DPBS (Dulbecco’s Phosphate Buffered Saline) before being trypsinized and harvested by centrifugation (250×g, 5 min). In each case, 10 μL were used to count cells. Cells were lysed in 1 mL 0.1 % Triton X-100 (Sigma, Taufkirchen, Germany). Half of each lysate was analyzed by SP-ICP-MS. The other half was digested for ICP-MS. The cell lysates and digested solutions were stored at 4 °C before analysis. Control samples without any cells were prepared using the same protocol.
For LA-ICP-MS, the cells (1 × 104 cells/cm2) were grown on polymer coated glass slides and incubated with NPs (2 µg/mL for Ag NPs or 2 and 10 µg/mL for TiO2 NPs) for 24 h. Cells were washed three times with DPBS and fixed with 4 % paraformaldehyde in DPBS. Therafter they were dehydrated in a series of ethanol (15, 30, 50, 70, 90 and 99.5 %). The slides were stored at 4 °C before analysis. Control cells without NPs were prepared similarly.
ICP-MS analysis of digested cells
For Ag NPs, 10 mL 65 % HNO3 was used for digesting cell lysates. For TiO2 NPs, 2 mL 65 % HNO3 and 4 mL 5 % HF was used. Digestion was performed in open vials at 60 °C using a heating block for 30 h. Total amounts of titanium and silver in the cells were determined by ICP-MS using a quadrupole ICP mass spectrometer (XSeries 2, Thermo Fisher Scientific GmbH, Dreieich, Germany). The ICP-MS parameters were optimized and are given in Additional file 1: Table S1. For the Ti and Ag detection, the 49Ti and 107Ag isotopes were selected. As an internal standard 115In was used. Digested samples were filled up with ultrapure water to 50 mL with 10 ppb of 115In as internal standard before analysis. Calibrations were performed using ionic Ti and Ag standards in 6.5 % HNO3 solution ranging from 0 to 20 μg/L for both elements. All experiments were conducted in three independent replicates for each treatment and control group. For the calculation of the number of NPs per cell, a perfect sphere was assumed for the particles and either TEM or DLS particle diameters were used.
SP-ICP-MS analysis of cell lysates
SP-ICP-MS was used to analyze number and size of NPs in the cell lysates (XSeries 2, Thermo Fisher Scientific GmbH, Dreieich, Germany). The SP-ICP-MS parameters were optimized and are given in Additional file 1: Table S1. Before analysis, the lysates were homogenized by vortexing and then diluted in ultrapure water to 50–100 ng/L Ag or Ti based on the ICP-MS measurements of digested cells, which were performed beforehand. For quality control of the nebulizer transport efficiency a freshly prepared 60 nm AuNP standard (NIST-RM 8013, Gaithersburg, MD, USA) was used at a concentration of 100 ng/L in ultrapure water, which yielded an average size of 61 nm (Additional file 1: Figure S6). The nebulizer transport efficiency ranged from 0.039 to 0.045.
For all measurements the instrument was operated in spike mode separately detecting 197Au, 107Ag and 48Ti isotopes one at a time. A constant sample flow rate of 0.34 mL/min was utilized. The duration time for each run was set at 1 min with a dwell time of 3 ms per reading. To determine the detector sensitivity in SP-ICP-MS for both elements, one point of each calibration series established by ICP-MS for digested cells (10 µg/L for Ag and Ti ion standard) was measured in spike mode. The limits of detection regarding the NP size (LODsize) of the TiO2 NPs and Ag NPs were calculated as described as follows with a 3σ threshold to identify the particle signal from the background noise :
Where σ is the standard deviation of the signal background (here: control group cell lysates); R is the sensitivity of the detector for the element of the analyte (cps/μg); f is the mass fraction of analyzed metal element in the NPs; ρ is the density of the NPs.
NP number limits of detection (LODnumberNP) were calculated by:
Where δneb is the nebulizer transport efficiency; βsam is the sample flow rate; and ti is the total acquisition time.
LA-ICP-MS of single cells
LA-ICP-MS was performed using an NWR 213 laser system (Electro Scientific Industries, Huntingdon, UK) coupled to an Element XR sector field ICP-MS (Thermo Fisher Scientific GmbH, Dreieich, Germany). The system was warmed up before analysis and tuned by ablating line scans with 200 µm spot size, 10 µm/s scan rate, 20 Hz repetition rate and 100 % laser energy from a microscope glass slide while optimizing the parameters for high signal intensities.
Glass slides were fixed in the ablation cell which mechanically moves the samples in xyz-direction under the fixed laser. At first, ablation parameters for dried cells were optimized to ensure complete ablation of the cells and a total coverage of the analyzed area which resulted in a scan speed of 5 µm/s, a spot size of 4 µm, a repetition rate of 10 Hz, a laser fluence of about 2.5 mj/cm2 and a lane distance of 5 µm, respectively. Details on the used equipment and the optimized parameters are given in Additional file 1: Table S2. To analyze sufficient numbers of cells, three different areas for each treatment and control group were evaluated. The aerosol was transported by a He carrier gas flow from the ablation cell to the ICP-MS where an additional Ar gas flow was introduced prior to the atomization and ionization in the plasma.
For quantification, two dilution series made from TiO2 NPs and Ag NPs in an untreated cell lysate matrix were prepared. The cell concentration was adjusted to theoretically 2 cells per µl (Additional file 1: Table S3). These solutions were then digested by adding nitric acid and hydrochloric acid (1:1) in an ultrasonic bath over night at 60 °C. 0.5 µl of each point of these dilution series were pipetted in duplicate onto a glass slide, dried and analyzed by LA-ICP-MS. For the quantification of this calibration series, ablation under the aforementioned parameters would be too time-consuming. Therefore, laser ablation for the calibration series was done with a higher scan speed of 200 µm/s, a bigger spot size of 250 µm and corresponding lane distance of 240 µm, and a higher laser fluence of about 2.5 mJ/cm2 (Additional file 1: Table S4).
In parallel, adjacent lines were ablated and the resulting time-dependent ICP-MS scans merged to one data set using lane distance, scan speed and time to calculate the dimensions. Integration of the signal intensity in the pipetted drops and in the cells was done using ImageJ software. Only clearly separated cells were used for integration and analysis. For the calculation of the number of NPs per cell a perfect sphere was assumed for the particles and the DLS size was used. Background correction for the cells and pipetted calibration was done for each slide using areas not containing any cells, cell compartments or droplets.
107Ag and/or 109Ag were detected for the Ag NPs. Despite its low abundance of 5.5 %, 49Ti was selected to conduct ICP-MS because it shows a low background noise and polyatomic interferences such as 33S16O or 31P18O can be resolved by the collision cell technique (CCT) of quadrupole ICP-MS . Higher abundant and therefore more sensitive 48Ti (73.8 %) was selected to conduct SP-ICP-MS  and LA-ICP-MS. For SP-ICP-MS, even though polyatomic interferences such as 32S16O and 36Ar12C or the isobaric interference with 48Ca are possible, these interferences only contribute to the continuous background while the TiO2 particles have distinct discontinuous signals and can thus be distinguished and isolated from the background. Our LODsize for 48Ti particles was 57 nm (equivalent to 69 nm TiO2), which was derived from background noise of cell lysates. Our LODsize was lower than for 49Ti (75 nm) and 47Ti (93 nm) particles, which was derived from water background by using the same instrument . For LA-ICP-MS, using a sector field ICP-MS allows resolving the polyatomic interferences for 48Ti but still does not suffice to distinguish it from 48Ca.
Two-tailed Student’s unpaired t–test was used for two-group comparison. p < 0.05 was considered statistically significant.
atomic absorption spectrometry
cell culture medium
collision cell technique
dynamic light scattering
Dulbecco’s phosphate buffered saline
energy-dispersive X-ray spectroscopy
human umbilical vein endothelial cells
inductively coupled plasma mass spectrometry
inductively coupled plasma optical emission spectrometry
laser ablation ICP-MS
limit of detection
single cell ICP-MS
single particle ICP-MS
scanning electron microscopy
transmission electron microscopy
Kessler R. Engineered nanoparticles in consumer products: understanding a new ingredient. Environ Health Perspect. 2011;119:a120–5.
Josset S, Keller N, Lett MC, Ledoux MJ, Keller V. Numeration methods for targeting photoactive materials in the UV-A photocatalytic removal of microorganisms. Chem Soc Rev. 2008;37:744–55.
Li WR, Xie XB, Shi QS, Zeng HY, Ou-Yang YS, Chen YB. Antibacterial activity and mechanism of silver nanoparticles on Escherichia coli. Appl Microbiol Biotechnol. 2010;85:1115–22.
Kowal K, Cronin P, Dworniczek E, Zeglinski J, Tiernan P, Wawrzynska M, Podbielska H, Tofail SAM. Biocidal effect and durability of nano-TiO2 coated textiles to combat hospital acquired infections. Rsc Adv. 2014;4:19945–52.
Veronovski N, Lesnik M, Lubej A, Verhovsek D. Surface treated titanium dioxide nanoparticles as inorganic UV filters in sunscreen products. Acta Chim Slov. 2014;61:595–600.
Chen XX, Cheng B, Yang YX, Cao AN, Liu JH, Du LJ, Liu YF, Zhao YL, Wang HF. Characterization and preliminary toxicity assay of nano-titanium dioxide additive in sugar-coated chewing gum. Small. 2013;9:1765–74.
Dubey A, Zai J, Qian X, Qiao Q. Metal oxide nanocrystals and their properties for application in solar cells. In: Bhushan B, Luo D, Schricker SR, Sigmund W, Zauscher S, editors. Handbook of nanomaterials properties. Berlin: Springer; 2014. p. 671–707.
Wilkinson LJ, White RJ, Chipman JK. Silver and nanoparticles of silver in wound dressings: a review of efficacy and safety. J Wound Care. 2011;20:543–9.
Larguinho M, Baptista PV. Gold and silver nanoparticles for clinical diagnostics—from genomics to proteomics. J Proteom. 2012;75:2811–23.
Reidy B, Haase A, Luch A, Dawson KA, Lynch I. Mechanisms of silver nanoparticle release, transformation and toxicity: a critical review of current knowledge and recommendations for future studies and applications. Materials. 2013;6:2295–350.
Shi HB, Magaye R, Castranova V, Zhao JS. Titanium dioxide nanoparticles: a review of current toxicological data. Part Fibre Toxicol. 2013;10:15.
Brown AP, Brydson RMD, Hondow NS. Measuring in vitro cellular uptake of nanoparticles by transmission electron microscopy. In: Nellist P, editor. Journal of physics conference series: electron microscopy and analysis group conference 2013, vol. 522. 2014. p. 250–4.
Gliga AR, Skoglund S, Wallinder IO, Fadeel B, Karlsson HL. Size-dependent cytotoxicity of silver nanoparticles in human lung cells: the role of cellular uptake, agglomeration and Ag release. Part Fibre Toxicol. 2014;11:11.
Klingberg H, Oddershede LB, Loeschner K, Larsen EH, Loft S, Moller P. Uptake of gold nanoparticles in primary human endothelial cells. Toxicol Res. 2015;4:655–66.
Schrand AM, Schlager JJ, Dai L, Hussain SM. Preparation of cells for assessing ultrastructural localization of nanoparticles with transmission electron microscopy. Nat Protoc. 2010;5:744–57.
Thurn KT, Arora H, Paunesku T, Wu A, Brown EM, Doty C, Kremer J, Woloschak G. Endocytosis of titanium dioxide nanoparticles in prostate cancer PC-3M cells. Nanomedicine. 2011;7:123–30.
Braun GB, Friman T, Pang HB, Pallaoro A, de Mendoza TH, Willmore AMA, Kotamraju VR, Mann AP, She ZG, Sugahara KN, et al. Etchable plasmonic nanoparticle probes to image and quantify cellular internalization. Nat Mat. 2014;13:904–11.
Salvati A, Aberg C, dos Santos T, Varela J, Pinto P, Lynch I, Dawson KA. Experimental and theoretical comparison of intracellular import of polymeric nanoparticles and small molecules: toward models of uptake kinetics. Nanomedicine. 2011;7:818–26.
Rashkow JT, Patel SC, Tappero R, Sitharaman B. Quantification of single-cell nanoparticle concentrations and the distribution of these concentrations in cell population. J R Soc Interface. 2014;11:5.
Krystek P, Kettler K, van der Wagt B, de Jong WH. Exploring influences on the cellular uptake of medium-sized silver nanoparticles into THP-1 cells. Microchem J. 2015;120:45–50.
Lu F, Wu SH, Hung Y, Mou CY. Size effect on cell uptake in well-suspended, uniform mesoporous silica nanoparticles. Small. 2009;5:1408–13.
Huang K, Ma H, Liu J, Huo S, Kumar A, Wei T, Zhang X, Jin S, Gan Y, Wang PC, et al. Size-dependent localization and penetration of ultrasmall gold nanoparticles in cancer cells, multicellular spheroids, and tumors in vivo. ACS Nano. 2012;6:4483–93.
Zheng LN, Wang M, Wang B, Chen HQ, Ouyang H, Zhao YL, Chai ZF, Feng WY. Determination of quantum dots in single cells by inductively coupled plasma mass spectrometry. Talanta. 2013;116:782–7.
Laborda F, Bolea E, Jimenez-Lamana J. Single particle inductively coupled plasma mass spectrometry: a powerful tool for nanoanalysis. Anal Chem. 2014;86:2270–8.
Drescher D, Giesen C, Traub H, Panne U, Kneipp J, Jakubowski N. Quantitative imaging of gold and silver nanoparticles in single eukaryotic cells by laser ablation ICP-MS. Anal Chem. 2012;84:9684–8.
Drescher D, Zeise I, Traub H, Guttmann P, Seifert S, Büchner T, Jakubowski N, Schneider G, Kneipp J. In situ characterization of SiO2 nanoparticle biointeractions using BrightSilica. Adv Func Mat. 2014;24:3765–75.
Bohme S, Stark HJ, Meissner T, Springer A, Reemtsma T, Kuhnel D, Busch W. Quantification of Al2O3 nanoparticles in human cell lines applying inductively coupled plasma mass spectrometry (neb-ICP-MS, LA-ICP-MS) and flow cytometry-based methods. J Nanopart Res. 2014;16:2592.
Buchner T, Drescher D, Traub H, Schrade P, Bachmann S, Jakubowski N, Kneipp J. Relating surface-enhanced Raman scattering signals of cells to gold nanoparticle aggregation as determined by LA-ICP-MS micromapping. Anal Bioanal Chem. 2014;406:7003–14.
Liu SC, Xu LJ, Zhang T, Ren GG, Yang Z. Oxidative stress and apoptosis induced by nanosized titanium dioxide in PC12 cells. Toxicology. 2010;267:172–7.
Haase A, Rott S, Mantion A, Graf P, Plendl J, Thunemann AF, Meier WP, Taubert A, Luch A, Reiser G. Effects of silver nanoparticles on primary mixed neural cell cultures: uptake, oxidative stress and acute calcium responses. Toxicol Sci. 2012;126:457–68.
Lee JH, Kim YS, Song KS, Ryu HR, Sung JH, Park JD, Park HM, Song NW, Shin BS, Marshak D, et al. Biopersistence of silver nanoparticles in tissues from Sprague-Dawley rats. Part Fibre Toxicol. 2013;10:36.
Huang CL, Hsiao IL, Lin HC, Wang CF, Huang YJ, Chuang CY. Silver nanoparticles affect on gene expression of inflammatory and neurodegenerative responses in mouse brain neural cells. Environ Res. 2015;136:253–63.
Wu CY, Tu KJ, Wu CH. High hydroxyl group density on the surface of TiO2 pretreated with alkaline hydrogen peroxide. In: Abstracts of papers of the American chemical society 2013; 246.
Deegan RD, Bakajin O, Dupont TF, Huber G, Nagel SR, Witten TA. Capillary flow as the cause of ring stains from dried liquid drops. Nature. 1997;389:827–9.
Bhardwaj R, Fang XH, Somasundaran P, Attinger D. Self-assembly of colloidal particles from evaporating droplets: role of DLVO interactions and proposition of a phase diagram. Langmuir. 2010;26:7833–42.
Ahlinder L, Ekstrand-Hammarstrom B, Geladi P, Osterlund L. Large uptake of titania and iron oxide nanoparticles in the nucleus of lung epithelial cells as measured by Raman imaging and multivariate classification. Biophys J. 2013;105:310–9.
Sengstock C, Diendorf J, Epple M, Schildhauer TA, Koller M. Effect of silver nanoparticles on human mesenchymal stem cell differentiation. Beilstein J Nanotech. 2014;5:2058–69.
Liu W, Wu Y, Wang C, Li HC, Wang T, Liao CY, Cui L, Zhou QF, Yan B, Jiang GB. Impact of silver nanoparticles on human cells: effect of particle size. Nanotoxicology. 2010;4:319–30.
Allouni ZE, Hol PJ, Cauqui MA, Gjerdet NR, Cimpan MR. Role of physicochemical characteristics in the uptake of TiO2 nanoparticles by fibroblasts. Toxicol In Vitro. 2012;26:469–79.
Zhu J, Liao L, Zhu L, Zhang P, Guo K, Kong J, Ji C, Liu B. Size-dependent cellular uptake efficiency, mechanism, and cytotoxicity of silica nanoparticles toward HeLa cells. Talanta. 2013;107:408–15.
Lee S, Bi X, Reed RB, Ranville JF, Herckes P, Westerhoff P. Nanoparticle size detection limits by single particle ICP-MS for 40 elements. Environ Sci Technol. 2014;48:10291–300.
Peters RJ, van Bemmel G, Herrera-Rivera Z, Helsper HP, Marvin HJ, Weigel S, Tromp PC, Oomen AG, Rietveld AG, Bouwmeester H. Characterization of titanium dioxide nanoparticles in food products: analytical methods to define nanoparticles. J Agric Food Chem. 2014;62:6285–93.
The study was planned by AH and JT, with input from all co-authors. ILH prepared all samples and performed cytotoxicity studies. ICP-MS and SP-ICPMS analysis was done by ILH with support of PR. LA-ICP-MS analysis was performed by FSB with support from ILH. Data analysis was done by ILH and FSB with input of NJ, JT and AH. The manuscript was written by ILH, FSB, AH with input of all co-authors. All authors read and approved the final manuscript.
The authors acknowledge funding from their institutes. In addition, I-Lun Hsiao thanks DAAD and the Ministry of Science and Technology Taiwan (MOST) for financial support. The authors thank Julian Tharmann for support with sample preparation and Tony Bewersdorff for help with nanoparticle characterization using NTA.
The authors declare that they have no competing interests.
Jutta Tentschert and Andrea Haase contributed equally to this work
About this article
Cite this article
Hsiao, I., Bierkandt, F.S., Reichardt, P. et al. Quantification and visualization of cellular uptake of TiO2 and Ag nanoparticles: comparison of different ICP-MS techniques. J Nanobiotechnol 14, 50 (2016). https://doi.org/10.1186/s12951-016-0203-z
- Single particle ICP-MS
- Laser ablation ICP-MS
- Cellular internalization