- Open Access
Intracellular fate of carbon nanotubes inside murine macrophages: pH-dependent detachment of iron catalyst nanoparticles
Particle and Fibre Toxicology volume 10, Article number: 24 (2013)
Carbon nanotubes (CNT) are a family of materials featuring a large range of length, diameter, numbers of walls and, quite often metallic impurities coming from the catalyst used for their synthesis. They exhibit unique physical properties, which have already led to an extensive development of CNT for numerous applications. Because of this development and the resulting potential increase of human exposure, an important body of literature has been published with the aim to evaluate the health impact of CNT. However, despite evidences of uptake and long-term persistence of CNT within macrophages and the central role of those cells in the CNT-induced pulmonary inflammatory response, a limited amount of data is available so far on the CNT fate inside macrophages. Therefore, the overall aim of our study was to investigate the fate of pristine single walled CNT (SWCNT) after their internalization by macrophages.
To achieve our aim, we used a broad range of techniques that aimed at getting a comprehensive characterization of the SWCNT and their catalyst residues before and after exposure of murine macrophages: X-ray diffraction (XRD), High Resolution (HR) Transmission Electron Microscopy (TEM), High Angle Annular Dark Field-Scanning TEM (HAADF-STEM) coupled to Electron Energy Loss Spectroscopy (EELS), as well as micro-X-ray fluorescence mapping (μXRF), using synchrotron radiation.
We showed 1) the rapid detachment of part of the iron nanoparticles initially attached to SWCNT which appeared as free iron nanoparticles in the cytoplasm and nucleus of CNT-exposed murine macrophages, and 2) that blockade of intracellular lysosomal acidification prevented iron nanoparticles detachment from CNT bundles and protected cells from CNT downstream toxicity.
The present results, while obtained with pristine SWCNT, could likely be extended to other catalyst-containing nanomaterials and surely open new ways in the interpretation and understanding of CNT toxicity.
Carbon nanotubes (CNT) are a family of nanomaterials featuring a large range of length, diameter, numbers of walls (single-walled -SWCNT-, double-walled -DWCNT- or multi-walled -MWCNT-) and, most often metallic impurities coming from the catalyst used for their synthesis. They exhibit unique physical properties, which have already led to their extensive use in composite materials . Moreover, prospective applications are also expected in electronics, for flat-panel displays, energy storage, water pollutants adsorbents, as well as in the nanomedicine field where CNT could be used for drug and non-viral gene delivery or for diagnosis . Due to the expansion of CNT usage and the resulting increase of potential human exposure, numerous investigations have, in recent years, aimed at evaluating the health impact of CNT in an occupational, environmental or biomedical context.
In vivo studies, essentially performed with animals exposed via the respiratory route have demonstrated that pulmonary exposure to CNT led to an immediate macrophage-mediated inflammatory response characterized mainly by a prominent macrophage influx in the bronchoalveolar fluid, together with an internalization of the CNT by the resident or attracted macrophages [3–8]. At later stages, respiratory exposure to CNT can lead to the development of pulmonary fibrosis and/or granuloma [9–13]. The presence of CNT in macrophages at the site of exposure or distributed throughout the body has been documented up to 24 months after the initial exposure . However, despite evidences of uptake and long-term persistence of CNT within macrophages, together with the central role of those cells in the CNT-induced inflammatory response, a limited amount of data is available so far on the fate of CNT inside macrophages. Whether internalized CNT are biopersistent or could be biotransformed have been indeed poorly investigated in macrophages. This is a critical and major gap in the actual knowledge because by-products resulting from the potential CNT transformation inside cells could have biological effects per se and thus be essential determinants in the toxicological profile of CNT.
The overall aim of our study was therefore to investigate the fate of SWCNT after their internalization by macrophages. We hypothesized that the residence of CNT inside cellular acidic compartments will lead to physicochemical and structural modifications of the internalized CNT. This was evaluated by using a broad range of techniques that aimed at getting a comprehensive characterization of the pristine SWCNT used, and of their metallic catalyst residues before and after exposure of murine macrophages. Our results show that 1) part of the iron-based catalyst nanoparticles initially attached to SWCNT rapidly appeared as free iron-based nanoparticles in the cytoplasm and nucleus of CNT-exposed murine macrophages, and that 2) the blockade of intracellular acidification processes prevented iron nanoparticles detachment from the CNT and also protected the cells from some potentially deleterious downstream effects induced by CNT. These data provide the first evidence of a biological processing of pristine CNT inside macrophages via a pH-dependent mechanism. Moreover, they also demonstrate the determinant role of by-products of this bio-processing in CNT toxicological profile.
Results and discussion
The diameter of the pristine SWCNT used in the present study has been previously evaluated by some of us  and estimated to be in the 0.8-1.2 nm range, while their individual length was in the 100–1000 nm range, according to supplier information. Thermogravimetric analysis measured an iron content of about 25-wt%, confirming the unpurified nature of the sample. X-ray diffraction (XRD) experiments revealed intense peaks at low wave-vector Q values characteristic of SWCNT organized in bundles (for a more detailed analysis, see ), while weaker peaks at higher wave-vectors corresponded to the signal of iron-based nanocrystals of cementite Fe3C (Figure 1a). No Bragg peak was observed at 1.8 Å-1, i.e. at wave-vectors corresponding to the stacking distance between the graphenic planes constitutive of graphite. This indicates that samples are free of graphitic impurities. Numerous iron-based particles (diameter in the 1–10 nm range), originating from the decomposition of iron pentacarbonyl during the synthesis, were present in the form of nanoparticles on the sidewalls of CNT, as observed in High Angle Annular Dark Field-Scanning Transmission Electron Microscopy (HAADF-STEM) and High Resolution Transmission Electron Microscopy (HRTEM) images (Figure 1b and 1c respectively). These residual iron nanoparticles were attached to CNT bundles through one or several carbon shells, as previously shown in ref. . The iron chemical nature of these nanoparticles was confirmed by Electron Energy Loss Spectroscopy (EELS), which exhibits a doublet of peaks corresponding to transitions from the Fe 2p core levels to the Fe 3d levels (Additional file 1: Figure S1).
To assess at the scale of several cells if SWCNT were present in SWCNT-exposed cells, we took advantage of iron catalyst residues attached to SWCNT and performed synchrotron-based micro X-ray fluorescence (μXRF) experiments on macrophages exposed to 0 (unexposed) or 50 μg/mL of pristine SWCNT. Figure 2a-i shows typical μXRF maps obtained for phosphorus (P) and iron (Fe) elements in unexposed (upper panel) and SWCNT-exposed macrophages (lower panel) after 24 hours exposure. The cellular shape can be drawn by the P map since phosphorus represents a characteristic element of cellular components . Moreover, endogenous iron was detectable and rather uniformly distributed in unexposed cells. For SWCNT-exposed cells, Fe maps presented both iron-rich zones co-localized with the P signal attributed to endogenous iron and specific iron-rich zones, close to the external border or outside the cells, which can be attributed to the CNT presence. Micro-XRF spectra integrated over regions where only cells were present (Figure 2a-ii) further confirmed the higher cellular content of iron associated with SWCNT exposure (red line), as compared to unexposed cells (black line). Similar results were obtained after 3 hours of exposure (data not shown).
To further evaluate the fate of SWCNT at the single cell and subcellular levels, we used HAADF-STEM to image cell sections after 3 or 24 hours of exposure. Figure 2b and c show typical HAADF-STEM images obtained with unexposed macrophages (Figure 2b and Additional file 2: Figure S2a) or with macrophages exposed to SWCNT over a 24 hours period (Figure 2c). Similar images were obtained after a 3 hours exposure (data not shown). Higher magnifications of cellular vesicles present in Figure 2c (orange and red squares, Figure 2d and e) clearly showed the presence of SWCNT bundles within the vesicles (inset Figure 2d), with small round nanoparticles (tiny white dots) attached to them, all along the CNT length. The chemical nature of these nanoparticles was checked using EELS measurements and displayed the characteristic Fe 2p to Fe 3d peak doublet of iron at 710 and 725 eV, similar to that found in the original material (Figure S1 and data not shown). Moreover, a typical image obtained in cytoplasmic and nuclear regions of cells exposed to SWCNT (zone containing cytoplasm and nucleus, as delimited by the blue square in Figure 2c) is shown in Figure 2f (and Additional file 2: Figure S2). Interestingly, it revealed isolated iron nanoparticles in both compartments; the chemical nature of the nanoparticles (i.e. iron) was here also confirmed by EELS analysis. In addition, the apparently free nanoparticles were similar in size to those initially attached to pristine CNT (1–10 nm, Figure 1b). It is noteworthy that we did not observe (HAADF-STEM and HRTEM analysis) any detachment of iron catalyst particles following CNT sample preparation (before cell exposure; gentle bath sonication treatment), which led us to conclude that detachment happened during (and probably because of) interaction with cells. To the best of our knowledge, such cellular detachment of metal based catalyst nanoparticles from CNT backbone has never been described in cells.
Apart from within vesicles, the intracellular localization of iron nanoparticles was mainly cytoplasmic, but a significant amount of these nanoparticles was also observed inside the nucleus after 24 hours. The quantification of the isolated nanoparticles showed that their total number significantly increased with time (from 3 to 24 hours), demonstrating a time-dependent process (Figure 2g). Interestingly, in cytoplasm and nucleus, iron nanoparticles did not appear to follow anymore the fibrillar shape of nanotube bundles as observed in vesicles (Figure 2d), but were rather isolated. Therefore, we further quantified the minimal distance between two nanoparticles in SWCNT before exposure, in SWCNT within vesicles, and in cytoplasm and nucleus (using ImageJ analysis of HAADF-STEM images; Figure 2h and 2i). As compared to what was observed with SWCNT (original material before cell exposure) or with SWCNT inside vesicles, the mean minimal distance between iron nanoparticles observed in the cytoplasm and/or nucleus was clearly higher (Figure 2h). In addition, the mean minimal distance was also slightly but significantly higher for iron nanoparticles observed in SWCNT-containing vesicles than for nanoparticles attached to SWCNT (Figure 2i). These results suggested that following the cellular uptake of CNT, the iron-based particles start to detach from the CNT backbone within the vesicles, and then translocate to the cytoplasm and eventually into the nucleus.
Because acidic treatment is a process commonly used to remove metallic impurities from as-produced pristine CNT samples [14, 18], we next hypothesized that the acidic environment present in phagolysosomes (pH 4.5) could be responsible for the detachment of the iron-based nanoparticles from the pristine CNT following their internalization. To test our hypothesis, we first assessed whether acidic phagolysosomes appeared in macrophages exposed to SWCNT. After 3 and 24 hours exposure to CNT, epi-fluorescence images displayed a concentration and the reorganization of acridine orange molecules coherent with an acidification of the lysosomes  (Figure 3a, and data not shown). The lysosomal activation was also confirmed by the dose-dependent significant increase in Cathepsin activity , observed in CNT-exposed macrophages (Figure 3b, p < 0.001 versus unexposed cells). Finally, the formation of phagolysosomes was further illustrated by the increased expression of two lysosomal proteins : Cathepsin B and Lysosome-Associated Membrane glycoprotein 1 (LAMP-1, Figure 3c and d, p < 0.05 exposed versus unexposed cells). Taken together, these results demonstrate the acidification of macrophage intracellular compartments after exposure to SWCNT.
To further address the role of acidification, we performed experiments in presence of Concanamycin A, a potent inhibitor of intracellular pH acidification . As shown in Figure 4a, μXRF maps and associated fluorescence spectra obtained in presence of Concanamycin A were similar to those obtained in absence of this inhibitor (Figure 2a-i), showing that the blockade of intracellular acidification did not prevent CNT uptake by macrophages. Nevertheless, the quantification of isolated iron nanoparticles showed that their total number significantly decreased in Concanamycin A-treated cells as compared to Concanamycin A non-treated cells, for both the nucleus and cytoplasm compartments (Figure 4b, p < 0.001 for treated versus untreated cells). This suggested that the detachment of nanoparticles and their subsequent distribution outside vesicles were related to pH acidification. Moreover, Concanamycin A treatment during CNT exposure was accompanied by a protection against CNT-induced phosphorylation of p53 and H2AX proteins which are both biomarkers for initiation of DNA repair processes  (Figure 4c and 4d). Those findings first indicated that inhibition of pH acidification protects macrophages from nuclear damages associated with SWCNT exposure. Secondly, they suggested that these deleterious effects might be related to the release of isolated nanoparticles from CNT due to the acidic environment inside lysosomes. We then further investigated whether the effects on DNA could be mediated by iron-related oxidative stress-dependent mechanisms. Expression of Ferritin heavy chain (H-Ferritin), which catalyzes the first step in ionic iron storage , and that of Heme Oxygenase (HO)-1 were both unmodified in macrophage exposure to SWCNT, in presence or absence of Concanamycin A (Additional file 3: Figure S3), which ruled out the possibility of an oxidative stress-driven mechanism.
Taken together, our results emphasize that, despite their initial encapsulation in carbon shells, catalyst iron nanoparticles can be detached from the SWCNT backbone via a pH-dependent mechanism and participate actively in the CNT-associated toxicity. Our study thus demonstrates for the first time that pristine CNT can be biologically modified inside macrophages via a lysosomal-dependent mechanism. Such results are particularly relevant in the context of an occupational exposure to as produced CNT, but are also likely to be part of a more global ability of macrophages to degrade carbon nanomaterial products.
In the last few years, different groups have demonstrated the possible enzyme-catalyzed oxidative biodegradation of CNT, although essentially in abiotic conditions [24–29]. However, these different studies focused mainly on the degradability of the graphitic lattices of CNT; and no specific data have been reported on the fate of the metal catalyst residues that are initially attached to the pristine CNT, although these residues are highly suspected to be essential determinants of the toxicological profile of non-purified CNT . Moreover, none of these studies have focused on the fate of CNT inside macrophages, despite the central role of macrophages in CNT-induced inflammatory response [3–8]. In the present study performed with pristine SWCNT, isolated iron-based nanoparticles were observed within exposed cells. Importantly, these isolated iron nanoparticles, although similar in size to those initially attached to pristine CNT, were not organized following CNT fiber shape. This individualization suggests that the iron nanoparticles were either not anymore linked to the CNT backbone, or that they were attached to a shorter CNT backbone that could result from a concomitant graphitic lattice oxidative biodegradation as previously described [24, 28, 30]. Although we cannot completely exclude a concomitant degradation of the backbone owing to the methodologies used in the present study, the first proposition is by far the most likely since the carbon shells around nanoparticles are much more defective than the backbone of pristine CNT themselves and will thus be submitted first to degradation processes . Indeed, defects or functionalized sites in the graphitic lattice of CNT appear to be mandatory to initiate the enzyme-mediated oxidative biodegradation of CNT backbone . Notably, enzyme-catalyzed biodegradation of pristine material was only possible after introduction of oxidative defects in the graphitic lattice . Although further studies are needed to fully characterize the mechanism of detachment observed here, our data strongly suggest a role for intracellular acidification in the detachment of iron nanoparticles, since Concanamycin A treatment abolished almost completely this event. We can also speculate that such acidification may allow the activation of pH-sensitive enzymes that could, in turn, attack the CNT backbone, but this hypothesis would need further investigations.
The presence of free and bioavailable iron nanoparticles in different cell compartments could have important pathophysiological consequences. The presence of small iron nanoparticles in the nuclear compartment suggests the possible penetration through ion channels or diffusion through pores in the nuclear membrane . Such event could have severe consequences in case of interaction with DNA , as suggested by the activation of p53 and H2AX pathways in our experimental settings, and could therefore explain the genotoxic effects often associated with CNT exposure [33–37]. Interestingly, iron oxide particles have been shown to dissolve inside murine alveolar macrophages , suggesting a potential additional mechanism of toxicity related to the interaction of soluble iron with proteins. However, since the intracellular levels of the iron storage protein H-Ferritin were not increased in SWCNT-exposed macrophages, the generation of ionic iron from the detached iron nanoparticles seems unlikely, at least within the timeframe of exposure used here. This was also further evidenced by the absence of HO-1 induction, suggesting the absence of an iron ion related oxidative stress-driven mechanism [39, 40]. Consequently, our data strongly support the idea that iron-based nanoparticles, and not solubilized iron, are important determinants of the SWCNT-induced biological effects observed in the present study.
In conclusion, our study provides the first evidence of biological transformation of SWCNT inside macrophages, as a result of an intracellular process governed by pH acidification, leading to catalyst nanoparticles detachment from CNT backbones. Our findings therefore demonstrate that although iron catalyst residues are initially isolated from biological media thanks to their surrounding carbon shells, they become more accessible to the biological environment owing to modifications following the uptake and residence of CNT bundles in acidic cell compartments. The present results, while obtained with pristine SWCNT, could likely be extended to other catalyst-containing nanomaterials and surely open new ways in the interpretation and understanding of CNT toxicity.
SWCNT were produced by the HiPCO process (HiPCO stands for ‘high pressure carbon monoxide’), which is a Chemical Vapor Deposition (CVD) process using continuous flowing carbon monoxide as the carbon feedstock and a small amount of iron pentacarbonyl as the iron-containing catalyst precursor at high pressure. Two batches of as-produced (raw grade) nanotubes were purchased from Carbon Nanotechnologies Incorporated (CNI® Buckytubes, Houston-TX, USA). Our high resolution transmission electron microscopy (HR-TEM) analysis (Akashi Topcon EM-002B microscope) has showed that iron is present in the form of nanoparticles on the side-walls of nanotube bundles , encapsulated in carbon shells . Pristine SWCNT used in the present study were similar to those used in ref   and , but came from different batches.
Carbon nanotube suspension
SWCNT were suspended at 250 μg/ml in serum-free cell culture medium (DMEM GlutaMAX™, Gibco LifeTechnologies). CNT suspensions were then rotated for 30 s, sonicated (RLI 275 sonication bath, LIREC, France) for 20 minutes under temperature-controlled conditions (+4°C), with 15 seconds interruption every 5 minutes for rotating steps. At the end of sonication, CNT suspensions were diluted at dedicated concentrations in serum-free cell culture medium, just before cell exposure. Scanning transmission electron microscopy (STEM) images (VG-HB501 microscope) were obtained on CNT before and after their gentle sonication and revealed no modification between the two samples.
Cell culture conditions
Murine macrophages (RAW 264.7 cell line, LGC Promochem/ ATCC) were cultured for 3 or 24 hours in cell culture medium (DMEM GlutaMAX™, Gibco LifeTechnologies) supplemented with 100 U/ml penicillin, 100 μg/ml streptomycin and 10% heat-inactivated foetal bovine serum (PAA Laboratories GmbH) under standard cell culture conditions (humidified incubator at 37°C under 5% CO2). In a subset of experiments, cells were pretreated for 1 hour with 10 nM Concanamycin A (Sigma-Aldrich, France) before CNT exposure. In all experiments, the volume of culture medium was calculated to be 200 μl/cm2 of cell surface. (i.e. 5 ml for a 25 cm2 culture flask).
X-ray diffraction (XRD) experiments were performed using a rotating molybdenium anode generator (Rigaku). The MoKα wavelength (λ = 0.711 Å) was chosen to minimize iron fluorescence (as compared to CuKα wavelength). It is selected using a doubly-bent graphite monochromator, ensuring high flux. Scattering by air being non negligible compared to that by CNT, experiments were performed under vacuum to optimize the signal/background ratio. CNT powder was placed in a glass capillary and studied in transmission. The data were recorded on planar imaging plates.
Thermogravimetric (TGA) analyses were performed under flowing air up to 1000°C (SETARAM apparatus) to determine the iron content in CNT powders by measuring the remaining weight corresponding to iron oxide after oxidative treatment.
Electron microscopy and spectroscopy
For ultrastructural observations, cells were seeded at 250 000 cells/ml on 60 mm diameter cell culture Petri dishes (TPP, ATGC biotechnologie, France) and cultured for 24 hours in serum condition before exposure. After 3 or 24 hours exposure to 10 μg/ml serum-free CNT suspensions or to serum-free cell culture medium, macrophages monolayer were fixed with 2% glutaraldehyde / 2% paraformaldehyde in cacodilate buffer, dehydrated, embedded in epoxy Resin (Epon 812) and then sectioned using an ultramicrotome at 40–50 nm on 400-mesh copper TEM grids for high resolution imaging by High Angle Annular Dark Field-Scanning TEM (HAADF-STEM). HAADF-STEM images were performed on a VG-HB501 microscope equipped with a tungsten cold field-emission gun operated at 100 keV with a sub-nanometer incident probe (0.5-1 nm). Electron Energy Loss Spectroscopy (EELS) spectra were recorded with a modified Gatan spectrometer. Spectra were recorded so as to cover a large energy range, with an energy resolution of about 1 eV. To highlight the presence of nanoparticles for their quantification, images were further processed using the ‘differentials’ tool named directional gradient (angle degree 0.0°) in Gatan digital micrograph software. Pixel intensities in each STEM pictures are related to the atomic number of the material imaged. Using this software tool, nanoparticles with high atomic number were thus highlighted compared to the background (biological material or resin with low atomic numbers). Quantitative evaluation of the minimal distance measurable between two catalyst particles (2–4 nm each) was performed using ImageJ software (National Institutes of Health, USA), on STEM images with the highest magnifications (see Figure 2f as an example), where resolution allows the clear identification of nanoparticles (40 images analyzed for each time points, 2 independent investigators). Two main compartments were considered for distance calculation: vesicles (with clearly identifiable SWCNT) and the rest of the cell (cytoplasm and nucleus). Particles that were on the edges of these compartments were excluded. Data are represented as individual points and median ± quartile. Quantitative evaluation of the number of isolated particles was realized manually by separating the distribution in two compartments (either cytoplasm, or nucleus). Only clearly individualized particles were numerated. The minimum distance between isolated nanoparticles was taken at 40 nm, which is the maximal distance observed for nanoparticles attached to SWCNT. The number of isolated nanoparticles was then normalized to the surface area of the different compartments, in μm2, where they were identified. Data are presented as mean ± SEM.
Synchotron-based microfluorescence experiments
For microfluorescence studies, murine cells were seeded at 250 000 cells/ml directly on thin window films used for micro X-ray fluorescence (XRF) studies  (Ultralene®, 4 μm thick, SPEX SamplePrep) and cultured for 24 hours as described above. These films were previously glued on specifically designed sample holders and sterilized by successive baths in 70° alcohol and antibiotics (penicillin/streptomycin). This biocompatible cell culture experimental system was put in 40 mm diameter cell culture Petri dishes and covered with cell suspension and cell culture medium. Twenty-four hours later, the cell culture medium was removed and the adherent cells monolayer was exposed for 3 to 24 hours to serum-free CNT suspensions (50 μg/ml), or to serum-free cell culture medium for unexposed samples, in presence or absence of 10 nM Concanamycin A.
At the end of exposure, cells were gently washed with 1× phosphate buffer saline (PBS, Gibco LifeTechnologies). Then, a quick wash with ultra-pure water (Sigma, Chromasolv® plus) was performed to remove salts coming from the culture medium. Immediately after, cells were further cryo-fixed and freeze-dried. Cryo-fixation was realized by rapid plunge of the cell culture system (cells on Ultralene film glued on sample holder) into an isopentane bath cooled with liquid nitrogen. Lyophilization was performed on a Christ Alpha 1–4 apparatus (ThermoFisher Scientific, Bioblock).
Synchrotron-based XRF microscopy experiments were performed on the ID21 beamline of the European Synchrotron Radiation Facility (ESRF, Grenoble, France). A fixed exit double crystal Si < 111 > monochromator (Kohzu) ensures a spectral resolution of 0.8 eV at 7.1 keV. Beam focalisation was assured by Kirkpatrick Baez (KB) mirrors allowing a beam size of 0.4*0.9 μm2. A silicon drift detector (Rontek) was used for fluorescence detection. An incident X-ray energy of 7.2 keV was chosen in order to excite the K-lines of elements of atomic number up to 26 (iron). All elements ranging from sodium (Z = 11) to iron (Z = 26) were detectable. Raster scans were performed across a chosen area of the sample preparation. From the analysis of the X-ray fluorescence spectrum for each pixel, a spatial image can be obtained for each element separately. Such an image represents a two-dimensional projection of the volumetric distribution of the elements. The vertical and horizontal pixel size was 0.5 μm each and data collection time for each pixel was about 0.5 s. Analysis of the fluorescence data has been performed in batch processing using the PyMca software .
Acridine orange stain
Cells were seeded at 50 000 cells/well in 8-well cell culture chamber slide (Lab Tek, Nunc, ATGC Biotechnology, France), and cultured for 24 hours in serum condition before exposure. They were further exposed to 50 μg/ml SWCNT in presence or in absence of 10 nM Concanamycin A for 3 to 24 hours in serum-free conditions. At the end of the exposure, cells were washed twice in PBS and further incubated with a 5 μg/ml solution of Acridine Orange (Sigma-Aldrich, France) for 15 min at 37°C. They were then rinsed three times in PBS, mounted with a DAPI-containing anti-fading solution (Vectashield H1200, Vector, France) and immediately observed under a confocal microscope (Zeiss LSM 510 Meta coupled to Zeiss AxioObserver Z1 inversed microscope). Excitation was at 488 nm, and emission was at 610 nm (lysosomes in red) and at 530 nm (DNA/RNA in green).
Cathepsin activity measurement
Cathepsin activity was measured using the cathepsin fluorogenic peptide substrate VII (R&D Systems, France), as previously described . Cells were seeded at 80 000 cells/well on 96-well plates (TPP, ATGC Biotechnology, France) and cultured as described above. They were exposed to 10 or 50 μg/ml SWCNT for 3 hours or 24 hours in presence or in absence of 10 nM Concanamycin A. At the end of exposure, 50 μl of cell supernatant was harvested and incubated for 1 h at 37°C with 27 μM of Cathepsin fluorogenic substrate. The activity was then measured using a fluorimeter (Infinite M200 Pro, TECAN, France), with an excitation set-up at 380 nm and emission at 460 nm. Results are represented as box and whisker plots of at least 3 repeated experiments.
LAMP-1 and Cathepsin B protein expression were evaluated on cell lysates obtained after exposure of macrophages to SWCNT for 3 to 24 hours, in presence or in absence of 10 nM Concanamycin A. Samples were separated by SDS-PAGE and were transferred onto PVDF membranes. Blots were incubated with goat anti mouse LAMP-1 (AF965, R&D Systems, France), mouse anti mouse Cathepsin B (AF4320, R&D Systems), rabbit anti Phospho-p53 (Ser-15, CST 9284S, Cell Signaling), mouse anti γH2AX (phospho S139, Abcam, France), goat anti H-Ferritin (sc-14416, Santa Cruz, France), or rabbit anti HO-1 (3001, Biomol, France). ß-actin was used as internal standard. Quantification of the expression of each protein was obtained using the ratio over ß-Actin expression. Results are represented as box and whisker plots of at least 3 repeated experiments.
Statistical evaluations were performed using GraphPad Prism software. As most of the data measured had a non-Gaussian distribution, the non-parametric Kruskall-Wallis test was used, with a Dunn’s Multiple Comparison post-hoc test when appropriated, or a Chi-square test. Significance was set at p < 0.05.
Ajayan PM, Tour JM: Materials science: nanotube composites. Nature 2007, 447: 1066–1068. 10.1038/4471066a
Lacerda L, Bianco A, Prato M, Kostarelos K: Carbon nanotubes as nanomedicines: from toxicology to pharmacology. Adv Drug Deliv Rev 2006, 58: 1460–1470. 10.1016/j.addr.2006.09.015
Mercer RR, Hubbs AF, Scabilloni JF, Wang L, Battelli LA, Schwegler-Berry D, Castranova V, Porter DW: Distribution and persistence of pleural penetrations by multi-walled carbon nanotubes. Part Fibre Toxicol 2011, 7: 28.
Murphy FA, Schinwald A, Poland CA, Donaldson K: The mechanism of pleural inflammation by long carbon nanotubes: interaction of long fibres with macrophages stimulates them to amplify pro-inflammatory responses in mesothelial cells. Part Fibre Toxicol 2012, 9: 8. 10.1186/1743-8977-9-8
Tabet L, Bussy C, Setyan A, Simon-Deckers A, Rossi MJ, Boczkowski J, Lanone S: Coating carbon nanotubes with a polystyrene-based polymer protects against pulmonary toxicity. Part Fibre Toxicol 2011, 8: 3. 10.1186/1743-8977-8-3
Boczkowski J, Lanone S: Respiratory toxicities of nanomaterials - a focus on carbon nanotubes. Adv Drug Deliv Rev 2012, 64: 1694–1699. 10.1016/j.addr.2012.05.011
Johnston HJ, Hutchison GR, Christensen FM, Peters S, Hankin S, Aschberger K, Stone V: A critical review of the biological mechanisms underlying the in vivo and in vitro toxicity of carbon nanotubes: the contribution of physico-chemical characteristics. Nanotoxicology 2010, 4: 207–246. 10.3109/17435390903569639
Donaldson K, Poland CA, Schins RP: Possible genotoxic mechanisms of nanoparticles: criteria for improved test strategies. Nanotoxicology 2010, 4: 414–420. 10.3109/17435390.2010.482751
Porter DW, Hubbs AF, Mercer RR, Wu N, Wolfarth MG, Sriram K, Leonard S, Battelli L, Schwegler-Berry D, Friend S, et al.: Mouse pulmonary dose- and time course-responses induced by exposure to multi-walled carbon nanotubes. Toxicology 2010, 269: 136–147. 10.1016/j.tox.2009.10.017
Mercer RR, Scabilloni J, Wang L, Kisin E, Murray AR, Schwegler-Berry D, Shvedova AA, Castranova V: Alteration of deposition pattern and pulmonary response as a result of improved dispersion of aspirated single-walled carbon nanotubes in a mouse model. Am J Physiol Lung Cell Mol Physiol 2008, 294: L87-L97.
Warheit DB, Laurence BR, Reed KL, Roach DH, Reynolds GA, Webb TR: Comparative pulmonary toxicity assessment of single-wall carbon nanotubes in rats. Toxicol Sci 2004, 77: 117–125.
Muller J, Huaux F, Moreau N, Misson P, Heilier JF, Delos M, Arras M, Fonseca A, Nagy JB, Lison D: Respiratory toxicity of multi-wall carbon nanotubes. Toxicol Appl Pharmacol 2005, 207: 221–231. 10.1016/j.taap.2005.01.008
Shvedova AA, Kisin ER, Mercer R, Murray AR, Johnson VJ, Potapovich AI, Tyurina YY, Gorelik O, Arepalli S, Schwegler-Berry D, et al.: Unusual inflammatory and fibrogenic pulmonary responses to single-walled carbon nanotubes in mice. Am J Physiol Lung Cell Mol Physiol 2005, 289: L698-L708. 10.1152/ajplung.00084.2005
Charron G, Mazerat S, Erdogan M, Gloter A, Filoramo A, Cambedouzou J, Launois P, Rivière E, Wernsdorfer W, Bourgoin JP, Mallah T: Insights into the mechanism of the gas-phase purification of HiPco SWNTs through a comprehensive multi-technique study. New J Chem 2009, 33: 1211–1223. 10.1039/b900373h
Chorro M, Kané G, Alvarez L, Cambedouzou J, Paineau E, Rossberg A, Kociak M, Aznar R, Pascarelli S, Launois P, Bantignies JL: 1D-confinement of polyiodides inside single-wall carbon nanotubes. Carbon 2013, 52: 100–108.
Heresanu V, Castro C, Cambedouzou J, Pinault M, Stephan O, Reynaud C, Mayne-L’hermite M, Launois P: Nature of the Catalyst Particles in CCVD Synthesis of Multiwalled Carbon Nanotubes Revealed by the Cooling Step Study. J Phys Chem C 2008, 112: 7371–7378. 10.1021/jp709825y
Bussy C, Cambedouzou J, Lanone S, Leccia E, Heresanu V, Pinault M, Mayne-L’hermite M, Brun N, Mory C, Cotte M, et al.: Carbon Nanotubes in Macrophages: Imaging and Chemical Analysis by X-ray Fluorescence Microscopy. Nano Lett 2008, 8: 2659–2663. 10.1021/nl800914m
Liu X, Guo L, Morris D, Kane AB, Hurt RH: Targeted Removal of Bioavailable Metal as a Detoxification Strategy for Carbon Nanotubes. Carbon N Y 2008, 46: 489–500. 10.1016/j.carbon.2007.12.018
Hamilton RF Jr, Wu N, Porter D, Buford M, Wolfarth M, Holian A: Particle length-dependent titanium dioxide nanomaterials’ toxicity and bioactivity. Part Fibre Toxicol 2009, 6: 35. 10.1186/1743-8977-6-35
Garin J, Diez R, Kieffer S, Dermine JF, Duclos S, Gagnon E, Sadoul R, Rondeau C, Desjardins M: The phagosome proteome: insight into phagosome functions. J Cell Biol 2001, 152: 165–180. 10.1083/jcb.152.1.165
Huss M, Wieczorek H: Inhibitors of V-ATPases: old and new players. J Exp Biol 2009, 212: 341–346. 10.1242/jeb.024067
Zhu L, Chang DW, Dai L, Hong Y: DNA damage induced by multiwalled carbon nanotubes in mouse embryonic stem cells. Nano Lett 2007, 7: 3592–3597. 10.1021/nl071303v
Evstatiev R, Gasche C: Iron sensing and signalling. Gut 2012, 61: 933–952. 10.1136/gut.2010.214312
Allen BL, Kichambare PD, Gou P, Vlasova II, Kapralov AA, Konduru N, Kagan VE, Star A: Biodegradation of single-walled carbon nanotubes through enzymatic catalysis. Nano Lett 2008, 8: 3899–3903. 10.1021/nl802315h
Kagan VE, Konduru NV, Feng W, Allen BL, Conroy J, Volkov Y, Vlasova II, Belikova NA, Yanamala N, Kapralov A, et al.: Carbon nanotubes degraded by neutrophil myeloperoxidase induce less pulmonary inflammation. Nat Nano 2010, 5: 354–359. 10.1038/nnano.2010.44
Liu X, Hurt RH, Kane AB: Biodurability of Single-Walled Carbon Nanotubes Depends on Surface Functionalization. Carbon N Y 2010, 48: 1961–1969. 10.1016/j.carbon.2010.02.002
Russier J, Menard-Moyon C, Venturelli E, Gravel E, Marcolongo G, Meneghetti M, Doris E, Bianco A: Oxidative biodegradation of single- and multi-walled carbon nanotubes. Nanoscale 2011, 3: 893–896. 10.1039/c0nr00779j
Kotchey GP, Hasan SA, Kapralov AA, Ha SH, Kim K, Shvedova AA, Kagan VE, Star A: A Natural Vanishing Act: The Enzyme-Catalyzed Degradation of Carbon Nanomaterials. Acc Chem Res 2012, 45: 1770–1781. 10.1021/ar300106h
Andon FT, Kapralov AA, Yanamala N, Feng W, Baygan A, Chambers BJ, Hultenby K, Ye F, Toprak MS, Brandner BD, et al.: Biodegradation of Single-Walled Carbon Nanotubes by Eosinophil Peroxidase. Small 2013. 10.1002/smll.201202508
Elgrabli D, Floriani M, Abella-Gallart S, Meunier L, Gamez C, Delalain P, Rogerieux F, Boczkowski J, Lacroix G: Biodistribution and clearance of instilled carbon nanotubes in rat lung. Part Fibre Toxicol 2008, 5: 20. 10.1186/1743-8977-5-20
Porter AE, Muller K, Skepper J, Midgley P, Welland M: Uptake of C60 by human monocyte macrophages, its localization and implications for toxicity: studied by high resolution electron microscopy and electron tomography. Acta Biomater 2006, 2: 409–419. 10.1016/j.actbio.2006.02.006
Kang B, Mackey MA, El-Sayed MA: Nuclear targeting of gold nanoparticles in cancer cells induces DNA damage, causing cytokinesis arrest and apoptosis. J Am Chem Soc 2010, 132: 1517–1519. 10.1021/ja9102698
Folkmann JK, Risom L, Jacobsen NR, Wallin H, Loft S, Moller P: Oxidatively damaged DNA in rats exposed by oral gavage to C60 fullerenes and single-walled carbon nanotubes. Environ Health Perspect 2009, 117: 703–708.
Jacobsen NR, Moller P, Jensen KA, Vogel U, Ladefoged O, Loft S, Wallin H: Lung inflammation and genotoxicity following pulmonary exposure to nanoparticles in ApoE−/− mice. Part Fibre Toxicol 2009, 6: 2. 10.1186/1743-8977-6-2
Jacobsen NR, Pojana G, White P, Moller P, Cohn CA, Korsholm KS, Vogel U, Marcomini A, Loft S, Wallin H: Genotoxicity, cytotoxicity, and reactive oxygen species induced by single-walled carbon nanotubes and C(60) fullerenes in the FE1-Mutatrade markMouse lung epithelial cells. Environ Mol Mutagen 2008, 49: 476–487. 10.1002/em.20406
Kisin ER, Murray AR, Keane MJ, Shi XC, Schwegler-Berry D, Gorelik O, Arepalli S, Castranova V, Wallace WE, Kagan VE, Shvedova AA: Single-walled carbon nanotubes: geno- and cytotoxic effects in lung fibroblast V79 cells. J Toxicol Environ Health A 2007, 70: 2071–2079. 10.1080/15287390701601251
Migliore L, Saracino D, Bonelli A, Colognato R, D’Errico MR, Magrini A, Bergamaschi A, Bergamaschi E: Carbon nanotubes induce oxidative DNA damage in RAW 264.7 cells. Environ Mol Mutagen 2010, 51: 294–303.
Beck-Speier I, Kreyling WG, Maier KL, Dayal N, Schladweiler MC, Mayer P, Semmler-Behnke M, Kodavanti UP: Soluble iron modulates iron oxide particle-induced inflammatory responses via prostaglandin E(2)synthesis: In vitro and in vivo studies. Part Fibre Toxicol 2009, 6: 34. 10.1186/1743-8977-6-34
Kagan VE, Tyurina YY, Tyurin VA, Konduru NV, Potapovich AI, Osipov AN, Kisin ER, Schwegler-Berry D, Mercer R, Castranova V, Shvedova AA: Direct and indirect effects of single walled carbon nanotubes on RAW 264.7 macrophages: Role of iron. Toxicol Lett 2006, 165: 88–100. 10.1016/j.toxlet.2006.02.001
Murray A, Kisin E, Leonard S, Young SH, Kommineni C, Kagan VE, Castranova V, Shvedova A: Oxidative stress and inflammatory response in dermal toxicity of single-walled carbon nanotubes. Toxicol 2009, 257: 161–171. 10.1016/j.tox.2008.12.023
Solé V, Papillon E, Cotte M, Walter P, Susini J: A multiplatform code for the analysis of energy-dispersive X-ray fluorescence spectra. Spectrochimica Actac Part B 2007, 62: 63–68. 10.1016/j.sab.2006.12.002
The authors thank Jean-Yves Bottero, Martine Mayne-L’Hermite, Périne Landois, Fabrice Valsaque and Odile Stéphan for useful comments and discussion. Fabrice Valsaque is also acknowledged for having performed some of the ATG measurements. CB and EP respectively acknowledge C’Nano Ile de France and RTRA ‘Triangle de la Physique’ for financial support of their fellowships. C’Nano-IdF is the nanoscience competence center of Paris Region, supported by CNRS, CEA, MESR, and Région Ile-de-France.
The authors have no competing interests to declare.
CB, JC, JB, PL and SL designed the study. CB, EB, LA and SL performed the biological assays. CB, EP, JC, MH, MP, BF, MS, SL and PL performed the physicochemical experiments. CB, NB and CM performed the microscopy observations. SL drafted the manuscript; CB, EP, JC, JB and PL were the main additional participants to its further elaboration. All authors approved the final manuscript.
Electronic supplementary material
Additional file 2: Figure S2: HAADF-STEM images of unexposed and SWCNT-exposed cells. Panel a: representative HAADF-STEM images of unexposed macrophages. Panel b: representative HAADF-STEM images of SWCNT-exposed macrophages (higher magnification on cytoplasmic region). Panel c: representative HAADF-STEM images of the nucleus of SWCNT-exposed macrophages. (PDF 185 KB)
Additional file 3: Figure S3: H-Ferritin and HO-1 expression. Panel a: typical western Blot image of H-Ferritin (23 kDa) and HO-1 (32 kDa) expression in macrophages exposed for 24 hours to SWCNT. ß-Actin is given as internal standard. Panel b: quantification of H-Ferritin and HO-1 expression in Western Blot, normalized to ß-Actin expression. (PDF 42 KB)
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Bussy, C., Paineau, E., Cambedouzou, J. et al. Intracellular fate of carbon nanotubes inside murine macrophages: pH-dependent detachment of iron catalyst nanoparticles. Part Fibre Toxicol 10, 24 (2013). https://doi.org/10.1186/1743-8977-10-24
- Carbon nanotubes
- Iron catalyst nanoparticles
- Lysosome acidification