Abstract
Relatively little is known about the fate of industrially relevant engineered nanomaterials (ENMs) in the lungs. Inhalation exposure and subsequent translocation of ENMs across the epithelial lining layer of the lung might contribute to clearance, toxic effects or both. To allow precise quantitation of translocation across lung epithelial cells, we developed a method for tracking industrially-relevant metal oxide ENMs in vitro using neutron activation. The versatility and sensitivity of the proposed In Vitro Epithelial Translocation (INVET) system was demonstrated using a variety of industry relevant ENMs including CeO2 of various primary particle diameter, ZnO, and SiO2-coated-CeO2 and ZnO particles. ENMs were neutron activated, forming gamma emitting isotopes 141Ce and 65Zn respectively. Calu-3 lung epithelial cells cultured to confluency on transwell inserts were exposed to neutron-activated ENM dispersions at sub-lethal doses to investigate the link between ENM properties and translocation potential. The effects of ENM exposure on monolayer integrity was monitored by various methods. ENM translocation across the cellular monolayer was assessed by gamma spectrometry following 2, 4 and 24 hours of exposure.
Our results demonstrate that ENMs translocated in small amounts (e.g. <0.01% of the delivered dose at 24 h), predominantly via transcellular pathways without compromising monolayer integrity or disrupting tight junctions. It was also demonstrated that the delivery of particles in suspension to cells in culture is proportional to translocation, emphasizing the importance of accurate dosimetry when comparing ENM-cellular interactions for large panels of materials. The reported INVET system for tracking industrially relevant ENMs while accounting for dosimetry can be a valuable tool for investigating nano-bio interactions in the future.
Keywords: nanotoxicology, in vitro, translocation, nanotechnology, dosimetry
INTRODUCTION
The increasing manufacture and use of engineered nanomaterials (ENMs) in electronics, cosmetics, toner formulations, and biomedical applications, raises questions regarding their environmental and occupational health and safety(Aitken, 2006, Bello et al., 2012, Pirela S et al., 2013). Human exposure via inhalation in particular is a growing concern. Studies have demonstrated inhaled ENMs can pass from the lungs into the bloodstream and enter extrapulmonary organs(Choi et al., 2010, Geiser et al., 2005, Kreyling et al., 2009), thereby increasing risk of cardiovascular morbidity and mortality(Brain et al., 2009, Mills et al., 2009). However, relatively little is known for industrially relevant ENMs regarding their fate, potential toxicity, and mechanisms of translocation in biological cells, tissues and organs(Kim YH et al., 2010, Yacobi et al., 2010).
Inhaled ENMs likely enter the systemic circulation across the alveolar epithelium, a very thin biological barrier (~0.5μm) that constitutes greater than 95% the surface area (~100m2 in humans) in distal airspaces of the lung(West, 2008). ENMs may translocate across the alveolar epithelium transcellularly via transcytosis (Conner and Schmid, 2003) and other nonendocytic mechanisms, or paracellularly via tight junctions. While hydrophilic solutes of hydrodynamic radius <6nm have been reported to passively translocate via paracellular pathways by restricted diffusion(Kim and Crandall, 1983, Matsukawa et al., 1997), nanoparticles greater than 10nm in diameter are expected to be excluded from tight junctions under normal conditions(Yacobi et al., 2010). If, however, ENM exposure disrupts tight junctions and compromises the epithelial monolayer barrier, paracellular transport could be increased. The effect of specific ENM properties on translocation across the alveolar epithelium, and whether transport occurs via a predominantly transcellular or paracellular pathway is not well-understood. The mechanism and extent of ENM translocation across epithelial monolayers hold implications for ENM clearance from the lungs as well as pulmonary and cardiovascular toxicity.
One major challenge in performing such studies is employing tracer particle models for tracking industrially relevant ENMs. Most in vitro studies utilize fluorescently labeled polystyrene beads for tracking particle-cell interactions(Rothen-Rutishauser et al., 2005, Yacobi et al., 2010, Xia et al., 2008b). These particles, however, are not representative of industrially relevant ENMs, are generated via wet-synthesis methods(Yang et al., 2013, Rothen-Rutishauser et al., 2005, Yacobi et al., 2010, Xia et al., 2008b), and there is low likelihood of inhalation exposure to these particles in aerosolized form. Furthermore, fluorescently labeled nanoparticles exhibit relatively low sensitivity for detecting small concentrations of particles, label instability, altered physicochemical properties such as surface chemistry and charge, and photobleaching from laser exposure(Tenuta et al., 2011, Sotiriou et al., 2012, Nel et al., 2009). Moreover, ENM transformations and agglomeration in liquid suspension and the subsequent effects on particle transport and delivery to cells in culture are often overlooked(Cohen et al., 2012, Teeguarden et al., 2007, Hinderliter et al., 2010, Deloid G et al., submitted July 2013)
An optimal tracer particle model for ENM translocation studies should enable tracking of industrially relevant ENMs. One particular class of ENMs with many industrial uses is flame generated metals and metal oxides. Flame-generated synthesis of ENMs is the currently preferred route by nanotechnology industry, and they account for the highest volume of ENMs in production(Wegner, 2003).
We present here a novel in vitro method for tracking ENM translocation across Calu-3 human lung epithelial monolayers. The proposed system utilizes well-characterized industrially relevant metal oxide ENMs, using a neutron activation technique. This radiotracer technique is a well-established method that enables tracking of flame-generated metal oxide nanoparticles for biodistribution studies in vivo, but has yet to be used extensively for in vitro studies(Chen JK, 2010, Yeh et al., 2012, He et al., 2010, Wang et al., 2010). A number of industry relevant ENMs such as CeO2 and ZnO nanoparticles were utilized in this study to show the versatility of the proposed method. Those ENMs were selected here due to their range in toxicity as well as their extensive presence in consumer products (including cosmetics, fuel additives, polishing slurries, etc.(Gass et al., 2013, Demokritou et al., 2013)). We also included “core shell” composite ENMs, consisting of either a CeO2 or ZnO core and a hermetic nano-thin coating of amorphous SiO2(Gass et al., 2013), in order to assess the effect of surface chemistry, particle size, and chemical composition on translocation across cellular monolayers.
MATERIALS AND METHODS
Nanomaterial synthesis and characterization
ENMs investigated are listed in Table 1. All ENMs were generated using the Harvard Versatile Engineered Nanomaterial Generation System (VENGES), as previously described (Demokritou et al., 2010, Sotiriou et al., 2011, Gass et al., 2013, Demokritou et al., 2013). ENMs were characterized for primary particle size and specific surface area. Specific surface area, SSA, defined as the area per mass (m2/g), was determined by the nitrogen adsorption/Brunauer-Emmett-Teller (BET) method (Micrometrics Tristar Norcross, GA, USA). The equivalent primary particle diameter, dBET, was calculated, assuming spherical particles, as:
| (1) |
where ρp is the particle density, which was obtained for each particle from the densities of component materials, at 20°C, reported in the CRC handbook of Chemistry and Physics (Haynes, 2012). Primary particle diameter was also determined by X-ray diffraction using a Scintag XDS2000 powder diffractometer (Cupertino, CA) (Cu Kα (λ = 0.154NM), −40 kV, 40 mA, step size = 0.02°) following previously described methods (Gass et al., 2013), and reported as dXRD (nm). Particle morphology and size were further characterized by transmission electron microscopy (TEM) (See Supplementary Figure 1) using a Libra 120 TEM (Zeiss, Oberkochen, Germany).
Table 1.
Characterization of ENM powders and liquid suspensions. SSA: (specific surface area) by nitrogen adsorption/Brunauer-Emmett-Teller (BET) method. dBET : particle diameter determined from SSA and particle density, ρ, as described in methods. dXRD : particle diameter by X-ray diffraction; ρ: material density; dH : hydrodynamic diameter, PdI: polydispersity index, ζ: zeta potential; πE: agglomerate effective density
| Material | SSA (m2/g) |
dBET (nm) |
dXRD (nm) |
ρ (g/cm3) |
Media | dH (nm) | ζ (mV) | ρE (g/cm3) |
|---|---|---|---|---|---|---|---|---|
| CeO2 - small dXRD=28.4nm |
28.0 | 28.0* | 28.4 | 7.65 | DI H2O | 136±1.06 | 34.5 ±3.15 | NA |
| MEM/5%FBS | 184±2.40 | −12.5±0.289 | 1.625 | |||||
| CeO2 - large dXRD=119nm |
11.0 31.3 |
71.9* 29.2 |
119 28.4 |
7.65 6.29 |
DI H2O | 231±2.93 | 34.5 ±3.15 | NA |
| MEM/5%FBS | 215±3.42 | −9.77±0.497 | 2.368 | |||||
| SiO2-coated CeO2 dXRD=28.4nm |
40.14 66.0 |
26.7 18.5 |
28.0 27.6 |
5.6 4.13 |
DI H2O | 208±2.87 | −26.8±0.277 | NA |
| MEM/5%FBS | 227±3.17 | −11.6±0.451 | 1.600 | |||||
| ZnO dXRD=28.0nm |
11.0 31.3 |
71.9* 29.2 |
119 28.4 |
7.65 6.29 |
DI H2O | 218±3.9 | 23.0±0.462 | NA |
| MEM/5%FBS | 235±2.55 | −15.5±3.29 | 1.485 | |||||
| SiO2-coated ZnO dXRD=27.6nm |
40.14 | 26.7 | 28.0 | 5.6 | DI H2O | 165±1.71 | −15.9±1.27 | NA |
| MEM/5%FBS | 206±4.52 | −12.6±5.77 | 1.655 |
dBET assumes spherical particles, CeO2 particles are hexagonal so dXRD is a more accurate description of primary particle size
ENM dispersal and characterization in liquid suspensions
ENM dispersion was performed using a protocol previously described by the authors and included calibration of sonication equipment to ensure accurate application and reporting of delivered sonication energy (DSE) in J/ml, as well as determination of the material specific critical delivered sonication energy (Cohen et al., 2012). ENMs were dispersed at 1 mg/ml in 10 ml of solute in 50 ml, conical polyethylene tubes, by sonication with a cup horn Branson Sonifier S-450A (Branson Ultrasonics, Danbury, CT) (maximum power output of 400 W at 60 Hz, continuous mode, output level 3, power delivered to sample: 1.25W). Dispersions were analyzed for hydrodynamic diameter (dH), polydispersity index (PdI), and zeta potential (ζ) by dynamic light scattering (DLS) using a Zetasizer Nano-ZS (Malvern Instruments, Worcestershire, UK). Stock solutions prepared in deionized water (DI H2O) were then diluted to desired concentrations (0, 6.25, 12.5, 25, 50, 100μg/ml) in cell culture media (MEM/5%FBS) prior to characterization for various particle and media parameters, or application to cells for toxicological evaluation.
Suspensions were also characterized for agglomerate effective density by the Harvard volumetric centrifugation method recently developed by the authors, described elsewhere(Deloid G et al., submitted July 2013, Demokritou P et al., 2012). In brief, one ml samples of 100 μg/ml suspensions of metal oxide ENMs were dispensed into TPP packed cell volume (PCV) tubes (Techno Plastic Products, Trasadingen, Switzerland) and centrifuged at 2,000 × g for one hour. Agglomerate pellet volumes, Vpellet, were measured, agglomerate densities were calculated from Vpellet values of triplicate samples for each ENM.
In vitro dosimetric considerations
The in vitro sedimentation, diffusion and dosimetry (ISDD) model proposed by Hinderliter et. al. and described previously (Hinderliter et al., 2010, Cohen et al., 2012) was used to calculate numerically for all ENMs studied, the fraction of administered particles that would be deposited onto cells as a function of time fD(t). The agglomerate hydrodynamic diameter, dH, the measured effective density were used as inputs to the model and are listed in Table 1. Additionally, the following parameters were used as inputs to the ISDD numerical model: Media column height, 1.5 mm; temperature, 310K; media density, 1.00 g/ml; viscosity, 0.00074 Pa s for MEM/5%FBS; and administered (initial suspension) particle concentration, 12.5μg/ml (Hinderliter et al., 2010).
Neutron activation of industry relevant ENMs
ENM powders were irradiated with neutrons for up to 24 hours at the Nuclear Reactor Laboratory (Massachusetts Institute of Technology, Cambridge, MA), and the radioactive 141Ce ENMs (CeO2, SiO2-coated CeO2), and 65Zn ENMs (ZnO, SiO2-coated ZnO) were stored in irradiation tubes. 141Ce and 65Zn are gamma emitters with a half-life of 32 days and 244 days respectively, and the successful production of radioactive ENMs following irradiation was confirmed by gamma energy spectrometry using a Packard gamma counter (Cobra Quantum, Packard Instrument, IL). ENMs were quantified as either percentage of total administered mass dose, or percentage of the estimated delivered dose, based on total measured radioactivity (counts per minute, CPM). Concentration calibrations were performed for each ENM by measuring radioactivity for a measured and known total ENM mass in suspension, and measuring radioactivity of dilutions by half down to 5ng.
Cell culture and cytotoxicity experiments
Immortalized human lung epithelial cells [CalU-3 (HTB-55), ATC, Manassas, VA] were cultured in Eagle’s Minimum Essential Medium (MEM) culture media supplemented with 5% heat inactivated fetal bovine serum (FBS), 100 U/ml penicillin, 100 μg/ml streptomycin, and 10mM HEPES. Culture media components were obtained from Sigma Aldrich (St. Louis, MO). All incubations were performed at 37°C/5% CO2. Cellular metabolic activity and cytotoxicity were measured via the 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyltetrazolium bromide (MTT) and lactate dehydrogenase (LDH) assay respectively according to the standard protocols previously reported (Demokritou et al., 2013; Gass et al., 2013). All experiments were conducted in triplicate for each ENM.
Absorbance values measured for LDH and MTT in vitro assays were normalized with negative control (particle free media) and positive control (Triton X-100; Sigma Aldrich, St. Louis, MO) absorbance values, to a metric of cell viability (%) using the following equation:
Variance of toxicity results for each ENM was tested by post hoc one-way ANOVA with significance set at p≤0.05. One-tailed unpaired student T test was used for significance testing, with significance set at p≤0.05.
Monitoring of formation and barrier integrity of cellular monolayer
Several methods were used to monitor the formation and integrity of cellular monolayers and tight junctions. In more detail:
Trans Epithelial Electrical Resistance (TEER)
Calu-3 cells were seeded at 5 × 105 cells per well onto 6.5mm Transwell ® tissue culture treated inserts (polyester membrane with 3.0 μm pores and 0.33 cm2 growth area) with 100μl of particle free MEM/5%FBS in the apical region and 600μl particle free MEM/5%FBS in the basal region, and cultured at 37°C in humidified air with 5% CO2. Resistance of the cell monolayer within each well, reported in ohms per cm2 of growth area (Ωcm2), was monitored daily prior to exposure using the Epithelial Voltohmeter and STX2 electrode (World Precision Instruments, Sarasota, FL), and the resistance of filters without cells was subtracted from all sample measurements. Wells reporting resistance greater than 500 Ωcm2 were assumed to have achieved monolayers with tight junctions, supported by previous findings in the literature(Geys et al., 2006, Geys et al., 2007, Rothen-Rutishauser et al., 2005),
Electrical Cell-substrate Impedance Sensing (ECIS)
In order to continuously monitor the electrical resistance of cellular monolayers cultured in vitro following exposure to industrially relevant ENMs, we utilized electrical cell-substrate impedance sensing (ECIS). Calu-3 cells were seeded onto ECIS 8W10E+ Cultureware slides (Applied BioPhysics, Inc, Troy, NY) with a growth area of 0.8cm2 at a density of 8 × 105 cells per well, and cultured in MEM/5%FBS at 37°C in humidified air with carbon dioxide. ECIS slides were connected to electrodes on the ECIS Model 1600R (Applied BioPhysics, Inc.), and resistance measurements were collected every 10 minutes. Once wells reached 2000Ω, culture media was replaced with ENM suspensions at a concentration of 12.5μg/ml, and resistance measurements were collected every 10 minutes for the next 48 hours. All experiments were conducted in triplicate.
Immunofluorescence staining
The effect of ENM exposure on cellular tight junctions was also assessed by immunofluorescence staining for intracellular tight junction protein zonula occludens-1 (ZO-1). In brief, following 24-hour exposure, transwells were washed in PBS, and cells were fixed in 3.7% formaldehyde (MeOH free, J.T. Baker, Phillipsburg, NJ) for 10 minutes at room temperature. Cells were then washed twice in PBS, and incubated with 50mM of glycine in PBS for 5 minutes at room temperature. Fixed cells were permeabilized and blocked with 0.5% saponin/1%BSA/1.5% goat serum for 30 minutes at room temperature. Rabbit antibody against ZO-1 (Invitrogen, Carslbad, CA) was diluted 1:100 in 0.5% saponin/1%BSA/1.5% goat serum and incubated with these monolayers at room temperature for 1.5 hours. Cells were then incubated with primary antibody (diluted in 0.5%saponin/1%BSA/1.5% goat serum at room temperature for 1.5 hours, followed by rinsing 3 times with 0.5% saponin in PBS at room temperature for 15 minutes. Monolayers were then incubated with secondary antibody [Alexa Fluor 488 goat-anti-rabbit IgG(H+L); Invitrogen, Carslbad, CA] diluted 1:100 in 0.5% saponin/1%BSA/1.5% goat serum for 1 hour at room temperature in the dark, followed by rinsing 3 times in 0.5%saponin/PBS for 15 minutes, and mounted on microscope slides with 20μl ProLong Gold antifade reagent with DAPI (Invitrogen, Carlsbad, CA). Monolayers not exposed to ENMs were similarly incubated with primary and secondary antibodies and processed, serving as negative controls. Images were acquired with a Zeiss Axioplan 200/Axiovert 200 confocal microscope system (Zeiss, Germany).
In Vitro Epithelial Translocation System (INVET)
The experimental setup for tracking translocation of industrially relevant ENMs across cellular monolayers in vitro is depicted in Figure 1. 100μl of ENM suspensions at a concentration of 12.5 μg/ml were applied to both transwells without cells, and transwells with Calu-3 cells cultured to confluence, for 2, 4, and 24 hours. The 12.5 μg/ml dose was pre-determined to be below the lethal dose via LDH and MTT cytotoxicity assays (Supplementary Figure 3). Following exposure, all supernatant and transwell inserts were collected from culture plates and set aside for analysis by gamma spectroscopy. All liquid present in the basolateral compartment of the transwell was then collected, and each basal well was washed 3 times with PBS and collected. Gamma counts were measured for apical compartments (including supernatant and the transwell insert), as well as for the basal compartment (including collected media and PBS wash) by gamma spectroscopy. A mass balance of ENMs measured in the apical and basal compartments was compared to gamma readings for ENM suspensions of equivalent total particle mass (1.25μg). All experiments were conducted in triplicate.
Figure 1.
Experimental setup of In Vitro Epithelial Translocation system (INVET).
TEM microscopy
Calu-3 cells were seeded onto 60mm tissue culture plates with a growth area of 28.0 cm2 at 2 × 105 cells/plate, and cultured in MEM/5%FBS at 37°C in humidified air with 5% CO2. Once cells formed a confluent layer, they were exposed to ENM suspensions at concentration of 12.5μg/ml. Following 24 hours exposure, cells were washed twice in PBS, removed from the culture plate with 0.25% Trypsin (Gibco, Carslbad, CA), and centrifuged at 1000 × g for 10 minutes.
Supernatant was decanted, and samples were fixed in Karnovsky’s fixative (2.5% Gluteraldehyde and 2.5% Paraformaldehyde in 0.1 M Soidum Cacodylate Buffer; Electron Microscopy Science, Hatfield, PA), then post-fixed in 2% Osmium Tetroxide (Electron Microscopy Science, Hatfield, PA) for one hour. Samples were then dehydrated and embedded in epon, the blocks were thin sectioned and stained with uranyl acetate and lead citrate (Electron Microscopy Science, Hatfield, PA). Images were photographed on a JEOL 1220 transmission electron microscope (Peabody, MA).
RESULTS
Nanomaterial characterization
Properties of ENM powders and dispersions used in this study are summarized in Table 1. Our nanopanel includes CeO2 ENMs of dXRD= 28.4 (CeO2 small) and dXRD= 119nm (CeO2 large), ZnO (dXRD=28.0nm), as well as SiO2-coated CeO2 of dXRD=28.4nm (CeO2 coated) and SiO2-coated ZnO of dXRD=27.6nm (ZnO coated). The variety of properties of the ENM panel allows for parametric comparison of the effects of primary particle size and surface chemistry on ENM translocation across cellular monolayers using the proposed INVET system. Representative electron microscopy images presented in Figure S1 illustrate the fractal structure of aggregates, indicative of flame generated ENMs. In the case of the SiO2 coated ENMs, a smooth and relatively homogenous 2-4nm SiO2 coated layer is visible around the core material (CeO2 and ZnO respectively). The hermetic encapsulation of the core ENMs by SiO2 with minimal effects on the core material has been previously described (Gass et al., 2013, Demokritou et al., 2013).
DLS characterization data presented in Table 1 demonstrates that in general, all ENMs formed agglomerates several times larger than their respective primary particle sizes in both DI H2O as well as cell culture media, with agglomerate diameters ranging from 200-230nm for all suspensions in MEM/5%FBS. ENM agglomerates were stable for up to 48 hours, the duration of our cellular exposures (data not shown), consistent with previous measurements for these materials (Gass et al., 2013, Cohen et al., 2012).
Effect of ENMs on monolayer barrier integrity
As described above and depicted in Figure 1, Calu-3 cell monolayers were cultured on transwell inserts, and monolayer development was monitored by TEER. Monolayer formation was determined when electrical resistance readings measured by TEER exceeded 500Ωcm2 (Supplementary Figure 3), consistent with previous reports in the literature(Geys et al., 2006, Geys et al., 2007).
Cellular monolayers with TEER≥500Ωcm2 were then exposed to ENMs at an administered dose of 12.5μg/ml, pre-determined to be below the lethal dose via LDH and MTT cytotoxicity assays (Supplementary Figure 4), which is consistent with toxicity results from the literature(Gass et al., 2013, Demokritou et al., 2013, Kroll et al., 2011, Xia et al., 2008a). Figure 2a presents TEER readings pre- and post-exposure at each time point, which suggest that ENM exposure did not result in a compromised monolayer and disturbance of tight junctions. Figure 2b presents the ECIS resistance measurements taken every 10 minutes following exposure, providing further support that ENM exposure at 12.5μg/ml does not compromise tight junctions or monolayer integrity. This data is consistent with previous studies investigating the effect of ZnO particles on cellular monolayers at similar administered mass concentrations (Kim YH et al., 2010).
Figure 2.
Effect of ENM exposure on monolayer electrical resistance. a)TEER of Calu-3 monolayers pre and post ENM exposure, error bars represent standard deviation; b) continuous resistance measurements via Electrical Cell-substrate Impedance Sensing (ECIS) during 48-hour exposure to ENM suspensions, error bars represent standard deviation.
Immunofluorescence staining for tight junction protein zonula occludens-1 (ZO-1) demonstrated negligible differences between Calu-3 monolayers exposed apically to 25μg/ml of each ENM suspension for 24 hours, compared with cells exposed to particle-free media (Supplementary Figure 5), suggesting ENM exposure leads to negligible disruption of continuity of tight junctions. These images are consistent with previously published confocal slices of ZO-1 stains, exhibiting high density of ZO-1 proteins principally at cell borders(Ye et al., 2009). This data further support our TEER and ECIS results, suggesting that ENM exposures at the low concentrations investigated do not compromise Calu-3 monolayer barrier function, nor do they disrupt tight junctions.
Tracking ENM translocation across cellular monolayers
ENM translocation across transwell filter membrane without cells – particle loss assessment
The ability of our ENM agglomerates to successfully pass through the 3μm pores of the transwell insert membrane in the absence of cells following 24-hour incubation was investigated in order to account for potential particle losses within the system. All five ENMs investigated easily permeated through the naked porous filter (<4% of the administered ENMs were collected from the transwell membrane, Supplementary Figure 6). A complete mass balance of administered particles was achieved for all ENMs, where the sum of ENMs measured in each compartment (supernatant, transwell membrane, and basolateral) was equal to the administered dose value, suggesting all ENMs are accounted for in our proposed in vitro translocation system (Supplementary Figure 6).
In vitro dosimetric considerations
The recently developed by the authors methodology to determine the delivered to cell dose was employed for all ENMs investigated (Deloid G et al., submitted July 2013), whereby ENM deposition in vitro via sedimentation and diffusion was estimated based on careful characterization of agglomerate parameters including hydrodynamic diameter and agglomerate effective density. Supplemental Figure 6 reports the estimated delivered to cell dose after 24 hours exposure for each material investigated, which in general strongly agreed with the translocated through the membrane dose for each material after 24 hours exposure (defined as the sum of ENMs measured on the transwell membrane and in the basolateral compartment), a clear indication of the validity of the proposed in vitro dosimetry methodology.
Figure 3 presents the estimated particle deposition curves over time for the three ENMs investigated for translocation across cellular monolayers at various time exposures. Large differences were estimated in the rate of particle delivery to cells across the ENMs studied. For example, after 24 hours exposure time, 99% of CeO2 large is delivered to cells, while only 58% of CeO2 small is delivered to cells. This discrepancy is largely due to differences in effective density of the two ENMs (2.368 and 1.365 g/cm3 respectively), which is directly related to sedimentation speed.
Figure 3.
Estimation of particle delivery to cells over 24-hour exposure period, f(24): fraction of administered dose delivered to cells following 24 hours exposure
ENM translocation across cellular monolayers
Figure 4a summarizes the amount of each ENMs detected in the basolateral compartment by gamma spectroscopy after 24 hour exposure duration using the INVET systems. These values are reported as both a percentage of the administered dose (Figure 4a), and normalized to the percentage of the delivered to cell dose based on the estimated delivered dose fractions (Figure 4b). Following 24 hours of exposure, very low amounts of each ENM were measured in the basolateral compartment (<0.01% administered dose) (Figure 4a). The results from ANOVA indicate the mean values for each ENM are statistically different from each other, though the low values of translocated particles make ranking the translocation potential of all ENMs investigated difficult. When dosimetry is taken into consideration, the difference between the two sized CeO2 particles (dXRD=28.4nm and 119nm respectively) is decreased, indicative of the importance of dosimetry in vitro. ZnO still exhibits the greatest translocation ability per delivered to cell dose (Figure 4b).
Figure 4.
Translocation of ENMs across cellular monolayer in vitro. a) Percent of administered dose measured in basolateral compartment of in vitro system following 24 hours exposure. b) Percent of delivered dose for ENMs measured in basolateral compartment following 24 hours exposure. All experiments were done in triplicate, error bars represent standard deviation. # indicates mean values for each material are not all equal (ANOVA) for p<0.05.
Figure 5 presents time resolved translocation data for CeO2 (for both primary particle sizes) and SiO2 coated CeO2 after 2, 4 and 24 hour exposure. Overall, very small amounts of all three ENMs successfully translocated into the basolateral compartment (<0.01%, Figure 5a). CeO2 large exhibited slightly greater translocation than CeO2 small at each time period. Additionally, for all three particles used here, increased translocation associated with increasing exposure duration from 4 to 24 hours was observed (e.g. CeO2 dXRD=28.4nm: 0.00038% vs 0.0020%). However, when normalized to delivered to cell dose, the amount of CeO2 small and CeO2 large measured in the basolateral compartment were found to be are roughly equal, and differences in translocation associated with increased exposure time also disappeared (Figure 5b). For example, after 24 hours exposure, the percent of delivered to cell particles (by mass) that translocated across the cellular monolayer for CeO2 small was 0.0035%, and for CeO2 large was 0.0030%. It is worth noting that SiO2 coated CeO2 exhibited greater translocation than both bare CeO2 particles even when normalized to the delivered dose (Figure 5b), a clear indication that surface chemistry plays an important role in translocation.
Figure 5.
a) Percent of administered dose for insoluble ENMs measured in basolateral compartment of in vitro system following 2, 4 and 24 hours exposure. b) Percent of delivered dose for insoluble ENMs measured in basolateral compartment following 2, 4 and 24 hours exposure. All experiments were performed in triplicate. Error bars represent standard deviation.
Cellular internalization of ENMs
Electron micrographs of cells exposed to ENMs for 24 hours were collected to determine the intracellular localization of ENM particles. Figure 6 presents representative images for Calu-3 cells exposed to CeO2 large (6a), and CeO2 small (6b). These images provide qualitative confirmation of cellular internalization, evidence that ENMs translocate across cellular monolayers via a predominantly transcellular pathway. In general, CeO2 ENMs appear encapsulated within membrane bound vacuoles. There appears to be greater quantities of CeO2 large particles internalized after 24 hour exposure, consistent with the estimated fast deposition rate and high delivered to cell dose estimated for this particle (Figure 3). It is worth noting that ENM aggregates appear concentrated within large endosomal vacuoles(Figure 6a). The CeO2 small particles appear internalized within later stage endosomal vacuoles, already fused with lysosomes and consolidated with other cellular debris. Similarly, representative images for the other particles provide evidence for cellular internalization and are included in Supplementary Figure 7.
Figure 6.
TEM images of ENMs internalized by Calu-3 cells following 24 hours exposure. a) CeO2 large; b) CeO2 small
DISCUSSION
Neutron activated tracer particle system
The data presented here illustrate the high sensitivity of the described radiolabel method which enables rapid and accurate detection of extremely small quantities of ENM in various in vitro systems. Furthermore, neutron activation has been shown to induce minimal effects on particle properties (He et al., 2010, Yeh et al., 2012). One limitation of the proposed particle system is the short half-life of some radioisotopes (141Ce, t1/2= 32 days), making necessary careful planning and time management of all cellular studies once ENMs have been irradiated.
Calu-3 In vitro model of alveolar epithelium
It must be noted that the Calu-3 human epithelial monolayer system used here is a simplified model of the alveolar region, consisting of type II alveolar epithelial cells which only account for <5% of the total surface area of the alveolar wall due to their distinct morphology, and are less likely to come into contact with inhaled ENMs than type I cells(West, 2008). Additionally, the distinct morphology of type II pneumocytes may have implications for particle-cell interactions in terms of the time required for particle endocytosis and exocytosis(West, 2008).
Furthermore, our monoculture model lacks phagocytic macrophages largely responsible for clearance and elimination of insoluble deposited particles through the tracheobronchial tree towards the larynx(Semmler et al., 2004, Kreyling et al., 2009, Geiser and Kreyling, 2010). It is worth noting that recent studies report non-specific and sporadic phagocytosis of TiO2 ENMs by alveolar macrophages in vivo, suggesting ENMs are able to evade a major clearance mechanism and that there is an increased likelihood for direct interactions with the alveolar epithelium(Geiser et al., 2008). Few nanotoxicology studies have developed 3 dimensional triple co-culture systems with primary epithelial cells, along with phagocytic macrophages and dendritic cells to simulate more realistic physiological conditions (Lehmann et al, 2011). Such sophisticated co-culture systems are necessary to improve the physiological relevance of in vitro translocation studies(Rothen-Rutishauser et al., 2005, Lehmann et al., 2011, Muller, 2011), and should be adopted in future studies to bring more physiological relevance to in vitro studies.
Translocation of industrially relevant ENMs using the proposed INVET system
It is clear from the aforementioned data that only small quantities of the ENMs used in this study are able to translocate transcellularly across Calu-3 cells without compromising the monolayer barrier or disrupting tight junctions. Yacobi et al recently reported similar findings after exposing rat alveolar epithelial cell monolayers to fluorescently labeled non-agglomerating polystyrene nanoparticles (PNPs)(Yacobi et al., 2010). However, PNP’s are not industrially relevant particles with high risk of inhalation exposure. The translocation potential of each ENM material used in this study are discussed in more detail below.
CeO2 ENMs
Both the size- and time-dependent differences in translocation are likely attributable to the differences in the delivered to cell dose of particles at each exposure time point. Limbach et al recently reported cellular uptake of CeO2 ENMs at low exposure concentrations may be limited to particle delivery to cells(Limbach, 2005). Indeed, when normalized to delivered dose, the amount of CeO2 small and CeO2 large we measured in the basolateral compartment are roughly equal, and differences in translocation associated with increased exposure time also disappear (Figure 5b). This data supports the theory that ENM-cell interactions in vitro largely depend on particle delivery to cells, emphasizing the importance of accurate dosimetry for in vitro nanotoxicology.
Our results for CeO2 are also consistent with previously reported findings indicating that extremely small quantities of CeO2 are able to translocate across a cellular monolayer quickly in vivo, with only small increases in total flux at longer exposure durations. A recent study investigating the biodistribution of CeO2 instilled in the lungs of Wister rats reported small quantities of CeO2 nanoparticles are capable of quickly accessing the bloodstream and entering transpulmonary organs within 10 minutes post exposure, though the majority of particles are persistent in the lungs weeks after instillation (64% of instilled particles remained in the lung at 28 days post exposure)(He et al., 2010). It is clear that CeO2 ENMs are able to translocate across cellular monolayers both in vitro and in vivo at extremely low levels, and translocation likely occurs via transcellular pathways.
SiO2 Coated ENMs
Both SiO2 coated CeO2 and SiO2 coated ZnO ENMs exhibited greater translocation than both bare CeO2 ENMs at 24 hours exposure (Figure 4a). SiO2 coated CeO2 exhibited greater translocation than bare CeO2 even when normalized to the delivered dose (Figure 4b), suggesting surface chemistry plays a significant role in ENM translocation across cellular monolayers. Increases in translocation associated with increasing exposure time (2, 4 and 24 hours) disappear when normalized to delivered dose (Figure 5), supporting the theory that ENM-cellular interactions are greatly influenced by particle delivery to cells and emphasizing the importance of dosimetry considerations for in vitro nanotoxicology.
Our findings for both SiO2 coated ENMs are consistent with recently reported in vivo investigations reporting translocation of pure SiO2 particles. Amorphous SiO2 ENMs of various primary particle size were instilled in the lungs of Wister rats at relatively high doses (2, 5 and 10mg/Kg by weight), and exhibited the ability to pass through the alveolar epithelium into systemic circulation and induce cardiovascular toxicity(Du et al., 2013). However, the exceedingly high doses used in this study may have resulted in lung particle overload and impaired alveolar macrophage mediated particle clearance, leading to increased particle accumulation in the lungs and increased potential for lung injury, compromise of the air-blood barrier and increased translocation events to occur(Oberdorster, 1995). In spite of this limitation, our results support the growing body-of-evidence that amorphous SiO2 particles and SiO2 coated ENMs are capable of translocation across the alveolar epithelium into the systemic circulation via transcellular pathways.
ZnO ENMs
ZnO exhibited the greatest amount of translocation following 24-hour exposure (Figure 4a). It is important to note that the measured translocation for ZnO ENMs does not distinguish between ZnO particles and Zn2+ ions associated with partial solubility of the ZnO. While Zhang et al recently reported 35% dissolution of ZnO ENMs following 24-hour incubation in cell culture media(Zhang et al., 2012), time-resolved solubility studies for this material will be required to determine the dissolution rate over time in cell culture media to further elucidate this issue. Significantly, ZnO particles of agglomerate diameter 230nm were measured by DLS in the basolateral media, providing evidence of particle translocation following 24-hour exposure. Future studies are required to further distinguish the translocation kinetics of particulate ZnO vs. translocation of zinc ions.
Cellular Internalization of ENMs
While our study provides some insight into understanding ENM translocation across epithelial barriers, more work is necessary to determine the mechanisms of cellular internalization. Several groups report a relationship between ENM properties (diameter, surface charge, etc) and endocytic mechansims, though often with conflicting results (Nel 2009). For example, Chithrani et al. reported an optimal diameter of 200nm for clathrin mediated uptake, and 500nm for caveolin mediated uptake (Chithrani et al. 2006). In contrast, Gratton et al. report the optimal diameter ranges from 50-80nm for clathrin mediated uptake, and is 120nm for caveolin mediated uptake (Gratton et al. 2008). With regards to particle translocation, Yacobi et al. reported higher translocation rates for amidine-modified polystyrene nanoparticles compared with carboxylate-modified PNPs, suggesting that direct interactions between PNPs and cell membranes may be the predominant mechanism for PNP internalization and translocation across primary rat alveolar epithelial cell monolayers (Yacobi et al. 2010).
It is clear that additional in vitro and in vivo studies are necessary to further elucidate the specific endocytic and exocytic mechanisms underlying translocation of industrially relevant ENMs, and our group is currently working to investigate these issues utilizing the developed INVET platform.
CONCLUSIONS
In this study we present a novel in vitro model for tracking the translocation of industrially relevant metal oxide ENMs across cellular monolayers in vitro. While neutron activated industrially relevant ENMs have been used for biodistribution studies in vivo, this is the first time such an approach has been used in vitro to assess particle-cell interactions. With the ever-increasing number and variety of engineered nanomaterials (ENMs) entering the consumer market, efficient and inexpensive in vitro models such as the one presented here are needed to correlate ENM properties with biological activity. The versatility and high sensitivity of this approach was demonstrated using a panel of industrially relevant ENMs of variable size and chemical composition and surface chemistry. We report that CeO2 of various primary particle sizes, ZnO, SiO2-coated CeO2 and SiO2-coated ZnO ENMs are able to translocate transcellularly across Calu-3 cellular monolayers at low doses, without compromising the alveolar epithelial barrier integrity, nor disrupting tight junctions at cell-cell borders. Electron micrographs of exposed cells exhibiting ENMs internalized by cells localized near large endosomal vacuoles provide supporting evidence that the translocation pathway is transcellular rather paracellular. Currently, there is indirect validation of our in vitro results published in the literature for each material based on instillation experiments in vivo. Additionally, our group is currently preparing manuscripts summarizing the results of in vivo pharmacokinetic studies investigating translocation of the particular materials used in our INVET system and reported on here. Though it was observed that very few particles were able to translocate across healthy cellular monolayers, the kinetics and mechanisms of ENM translocation may be different for unhealthy monolayers with disrupted tight junctions. For example, ozone exposure is known to increase the permeability of the air blood barrier, with implications for increased translocation of ENM particles. Furthermore, the results of this study highlight the importance of dosimetry for accurate in vitro nanotoxicity studies. Although additional in vitro and in vivo studies are required to further elucidate the specific endocytic and exocytic mechanisms underlying ENM translocation at physiologically relevant exposure doses, it is clear that industrially relevant metal oxide ENMs are capable of crossing healthy alveolar monolayers without compromising the epithelium barrier integrity.
Supplementary Material
ACKNOWLEDGEMENTS
This research project was supported by NIEHS grant (ES-0000002), NSF grant (ID 1235806) and the Center for Nanotechnology and Nanotoxicology at The Harvard School of Public Health.
Footnotes
DISCLAIMER
The findings and conclusions in this report are those of the authors and do not necessarily represent the views of the National Institute for Occupational Safety and Health
DECLARATIONS OF INTEREST
The authors declared no personal interests related to this study.
REFERENCES
- PROJECT ON EMERGING NANOTECHNOLOGIES; W. W. I. C. F. S., editor. The Nanotechnology Consumer Product Inventory. 2011. [Google Scholar]
- AITKEN R, C MQ, BOXALL ABA, HULL M. Manufacture and use of nanomaterials: Current status in the UK and global trends. Occup Med. 2006;56(7):300–306. doi: 10.1093/occmed/kql051. [DOI] [PubMed] [Google Scholar]
- BELLO D, MARTIN J, SANTEUFEMIO C, SUN Q, LEE BUNKER K, SHAFER M, DEMOKRITOU P. Physicochemical and morphological characterisation of nanoparticles from photocopiers: implications for environmental health. Nanotoxicology. 2012 doi: 10.3109/17435390.2012.689883. doi: 10.3109/17435390.2012.689882. [DOI] [PubMed] [Google Scholar]
- BRAIN J. Biologic responses to nanomaterials depend on exposure, clearance, and material characteristics. Nanotoxicology. 2009;3:1–7. [Google Scholar]
- CHEN JK, S M, PIER JJ, LIUE CH, CHOU FI, LAI WH, CHANG LW, LIN P, WANG MY, YANG MH, YANG CS. The use of radioactive zinc oxide nanoparticles in determination of their tissue concentrations following intravenous administration in mice. Analyst. 2010;135:1742–1746. doi: 10.1039/c0an00110d. [DOI] [PubMed] [Google Scholar]
- CHITHRANI BD, GHAZANI AA, CHAN WCW. Determining the size and shape dependence of gold nanoparticle uptake into mammalian cells. Nano Lett. 2006;6:662–668. doi: 10.1021/nl052396o. [DOI] [PubMed] [Google Scholar]
- CHOI HS, ASHITATE Y, LEE JH, KIM SH, MATSUI A, INSIN N, BAWENDI MG, SEMMLER-BEHNKE M, FRANGIONI JV, TSUDA A. Rapid translocation of nanoparticles from the lung airspaces to the body. Nat Biotechnol. 2010;28:1300–3. doi: 10.1038/nbt.1696. [DOI] [PMC free article] [PubMed] [Google Scholar]
- COHEN J, DELOID G, PYRGIOTAKIS G, DEMOKRITOU P. Interactions of Engineered Nanomaterials in Physiological Media and Implications for In Vitro Dosimetry. Nanotoxicology. 2012 doi: 10.3109/17435390.2012.666576. doi: 10.3109/17435390.2012.666576. [DOI] [PMC free article] [PubMed] [Google Scholar]
- CONNER SD, SCHMID SL. Regulated portals of entry into the cell. Nature. 2003;422:37–44. doi: 10.1038/nature01451. [DOI] [PubMed] [Google Scholar]
- DELOID G, C J, DARRAH T, DERK R, ROJANASAKUL L, PYRGIOTAKIS G, WOHLLEBEN W, DEMOKRITOU P. Estimating effective density of engineered nanomaterials for in vitro dosimetry. Nature Communications. 2013 Jul; doi: 10.1038/ncomms4514. submitted. [DOI] [PMC free article] [PubMed] [Google Scholar]
- DEMOKRITOU P, BUCHEL R, MOLINA RM, DELOID GM, BRAIN JD, PRATSINIS SE. Development and characterization of a Versatile Engineered Nanomaterial Generation System (VENGES) suitable for toxicological studies. Inhal Toxicol. 2010;22(Suppl 2):107–16. doi: 10.3109/08958378.2010.499385. [DOI] [PMC free article] [PubMed] [Google Scholar]
- DEMOKRITOU P, C J, DELOID G. Novel Methods of Measuring Effective Density of Nanoparticles in Fluids. U.S. patent application 61/661,895. 2012
- DEMOKRITOU P, GASS S, PYRGIOTAKIS G, COHEN JM, GOLDSMITH W, MCKINNEY W, FRAZER D, MA JY, SCHWEGLER-BERRY D, BRAIN JD, CASTRANOVA V. An in vivo and in vitro toxicological characterization of realistic nanoscale CeO2 inhalation exposures. Nanotoxicology. 2013 doi: 10.3109/17435390.2012.739665. doi: 10.3109/17435390.2012.739665. [DOI] [PMC free article] [PubMed] [Google Scholar]
- DU Z, ZHAO D, JING L, CUI G, JIN M, LI Y, LIU X, LIU Y, DU H, GUO C, ZHOU X, SUN Z. Cardiovascular Toxicity of Different Sizes Amorphous Silica Nanoparticles in Rats After Intratracheal Instillation. Cardiovasc Toxicol. 2013;13(3):194–207. doi: 10.1007/s12012-013-9198-y. [DOI] [PubMed] [Google Scholar]
- GASS S, COHEN JM, PYRGIOTAKIS G, SOTIRIOU GA, BUECHEL R, PRATSINIS SE, DEMOKRITOU P. A safer formulation concept for flame-generated engineered nanomaterials. ACS Sustainable Chemistry & Engineering. 2013;1(7):843–857. doi: 10.1021/sc300152f. [DOI] [PMC free article] [PubMed] [Google Scholar]
- GEISER M, CASAULTA M, KUPFERSCHMID B, SCHULZ H, SEMMLER-BEHNKE M, KREYLING W. The role of macrophages in the clearance of inhaled ultrafine titanium dioxide particles. Am J Respir Cell Mol Biol. 2008;38:371–6. doi: 10.1165/rcmb.2007-0138OC. [DOI] [PubMed] [Google Scholar]
- GEISER M, KREYLING WG. Deposition and biokinetics of inhaled nanoparticles. Part Fibre Toxicol. 2010;7:2. doi: 10.1186/1743-8977-7-2. doi: 10.1186/1743-8977-7-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- GEISER M, ROTHEN-RUTISHAUSER B, KAPP N, SCHURCH S, KREYLING W, SCHULZ H, SEMMLER M, IM HOF V, HEYDER J, GEHR P. Ultrafine particles cross cellular membranes by nonphagocytic mechanisms in lungs and in cultured cells. Environ Health Perspect. 2005;113:1555–60. doi: 10.1289/ehp.8006. [DOI] [PMC free article] [PubMed] [Google Scholar]
- GEYS J, COENEGRACHTS L, VERCAMMEN J, ENGELBORGHS Y, NEMMAR A, NEMERY B, HOET PH. In vitro study of the pulmonary translocation of nanoparticles: a preliminary study. Toxicol Lett. 2006;160:218–26. doi: 10.1016/j.toxlet.2005.07.005. [DOI] [PubMed] [Google Scholar]
- GEYS J, NEMERY B, HOET PH. Optimisation of culture conditions to develop an in vitro pulmonary permeability model. Toxicol In Vitro. 2007;21:1215–9. doi: 10.1016/j.tiv.2007.05.012. [DOI] [PubMed] [Google Scholar]
- GRATTON SEA, ROOP PA, POHIHAUS PD, LUFT JC, MADDEN VJ, NAPIER ME, DESIMONE JM. The effect of particle design on cellular internalization pathways. Proc. Natl Acad Sci USA. 2008;105:11613–11618. doi: 10.1073/pnas.0801763105. [DOI] [PMC free article] [PubMed] [Google Scholar]
- HAYNES WM. CRC Handbook of Chemistry and Physics. 92nd edition CRC Press; Boca Raton, FL: 2012. [Google Scholar]
- HE X, ZHANG H, MA Y, BAI W, ZHANG Z, LU K, DING Y, ZHAO Y, CHAI Z. Lung deposition and extrapulmonary translocation of nano-ceria after intratracheal instillation. Nanotechnology. 2010;21:285103–285111. doi: 10.1088/0957-4484/21/28/285103. [DOI] [PubMed] [Google Scholar]
- HINDERLITER PM, MINARD KR, ORR G, CHRISLER WB, THRALL BD, POUNDS JG, TEEGUARDEN JG. ISDD: A computational model of particle sedimentation, diffusion and target cell dosimetry for in vitro toxicity studies. Part Fibre Toxicol. 2010;7 doi: 10.1186/1743-8977-7-36. doi: 10.1186/1743-8977-7-36. [DOI] [PMC free article] [PubMed] [Google Scholar]
- KIM KJ, CRANDALL ED. Heteropore populations of bullfrog alveolar epithelium. J Appl Physiol. 1983;54:140–6. doi: 10.1152/jappl.1983.54.1.140. [DOI] [PubMed] [Google Scholar]
- KIM YH, F F, KENNEDY IM, YACOBI NR, HAMM-ALVAREZ SF, BOROK ZEA, KIM KJ, CRANDALL ED. Alveolar Epithelial Cell Injury Due to Zinc Oxide Nanoparticle Exposure. Am J Respir Crit Care Med. 2010;182:1398–1409. doi: 10.1164/rccm.201002-0185OC. [DOI] [PMC free article] [PubMed] [Google Scholar]
- KREYLING WG, SEMMLER-BEHNKE M, SEITZ J, SCYMCZAK W, WENK A, MAYER P, TAKENAKA S, OBERDORSTER G. Size dependence of the translocation of inhaled iridium and carbon nanoparticle aggregates from the lung of rats to the blood and secondary target organs. Inhal Toxicol. 2009;21(Suppl 1):55–60. doi: 10.1080/08958370902942517. [DOI] [PubMed] [Google Scholar]
- KROLL A, DIERKER C, ROMMEL C, HAHN D, WOHLLEBEN W, SCHULZE-ISFORT C, GOBBERT C, VOETZ M, HARDINGHAUS F, SCHNEKENBURGER J. Cytotoxicity screening of 23 engineered nanomaterials using a test matrix of ten cell lines and three different assays. Particle and Fibre Toxicology. 2011;8 doi: 10.1186/1743-8977-8-9. doi: 10.1186/1743-8977-8-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
- LEHMANN AD, DAUM N, BUR M, LEHR CM, GEHR P, ROTHEN-RUTISHAUSER BM. An in vitro triple cell co-culture model with primary cells mimicking the human alveolar epithelial barrier. Eur J Pharm Biopharm. 2011;77:398–406. doi: 10.1016/j.ejpb.2010.10.014. [DOI] [PubMed] [Google Scholar]
- LIMBACH L. 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. doi: 10.1021/es051043o. [DOI] [PubMed] [Google Scholar]
- MATSUKAWA Y, LEE VH, CRANDALL ED, KIM KJ. Size-dependent dextran transport across rat alveolar epithelial cell monolayers. J Pharm Sci. 1997;86:305–9. doi: 10.1021/js960352x. [DOI] [PubMed] [Google Scholar]
- MILLS NL, DONALDSON K, HADOKE PW, BOON NA, MACNEE W, CASSEE FR, SANDSTROM T, BLOMBERG A, NEWBY DE. Adverse cardiovascular effects of air pollution. Nat Clin Pract Cardiovasc Med. 2009;6:36–44. doi: 10.1038/ncpcardio1399. [DOI] [PubMed] [Google Scholar]
- MULLER L, G M, RAEMY DO, HERZOG F, BRANDENBERGER C, SCHMID O, GEHR P, ROTHEN-RUTISHAUSER B, CLIFT MJD. Realistic Exposure Methods for Investigating the Interaction of Nanoparticles with the Lung at the Air-Liquid Interface In Vitro. Insciences. 2011;1:30–64. [Google Scholar]
- NEL AE, MADLER L, VELEGOL D, XIA T, HOEK EM, SOMASUNDARAN P, KLAESSIG F, CASTRANOVA V, THOMPSON M. Understanding biophysicochemical interactions at the nano-bio interface. Nat Mater. 2009;8:543–57. doi: 10.1038/nmat2442. [DOI] [PubMed] [Google Scholar]
- OBERDORSTER G. Lung particle overload: implications for occupational exposures to particles. Regul Toxicol Pharmacol. 1995;21:123–35. doi: 10.1006/rtph.1995.1017. [DOI] [PubMed] [Google Scholar]
- PIRELA S, M R, WATSON C, COHEN JM, BELLO D, DEMOKRITOU P, BRAIN J. Effects of copy center particles on the lungs: a toxicological characterization using a Balb/c mouse model. Inhal Toxicol. 2013;25(9):498–508. doi: 10.3109/08958378.2013.806614. [DOI] [PMC free article] [PubMed] [Google Scholar]
- ROTHEN-RUTISHAUSER BM, KIAMA SG, GEHR P. A three-dimensional cellular model of the human respiratory tract to study the interaction with particles. Am J Respir Cell Mol Biol. 2005;32:281–9. doi: 10.1165/rcmb.2004-0187OC. [DOI] [PubMed] [Google Scholar]
- SEMMLER M, SEITZ J, ERBE F, MAYER P, HEYDER J, OBERDORSTER G, KREYLING WG. Long-term clearance kinetics of inhaled ultrafine insoluble iridium particles from the rat lung, including transient translocation into secondary organs. Inhal Toxicol. 2004;16:453–9. doi: 10.1080/08958370490439650. [DOI] [PubMed] [Google Scholar]
- SOTIRIOU GA, DIAZ E, LONG MS, GODLESKI J, BRAIN J, PRATSINIS SE, DEMOKRITOU P. A novel platform for pulmonary and cardiovascular toxicological characterization of inhaled engineered nanomaterials. Nanotoxicology. 2011;11:680–690. doi: 10.3109/17435390.2011.604439. [DOI] [PMC free article] [PubMed] [Google Scholar]
- SOTIRIOU GA, F D, POULIKAKOS D, FERRARI A. Optically Stable Biocompatible Flame-Made SiO2-Coated Y2O3: Tb3+ Nanophosphors for Cell Imaging. ACS Nano. 2012;6:680–690. doi: 10.1021/nn205035p. [DOI] [PMC free article] [PubMed] [Google Scholar]
- TEEGUARDEN JG, HINDERLITER PM, ORR G, THRALL BD, POUNDS JG. Particokinetics in vitro: dosimetry considerations for in vitro nanoparticle toxicity assessments. Toxicol Sci. 2007;95:300–12. doi: 10.1093/toxsci/kfl165. [DOI] [PubMed] [Google Scholar]
- TENUTA T, MONOPOLI MP, KIM J, SALVATI A, DAWSON KA, SANDIN P, LYNCH I. Elution of labile fluorescent dye from nanoparticles during biological use. PLoS One. 2011;6(10) doi: 10.1371/journal.pone.0025556. doi: 10.1371/journal.pone.0025556. [DOI] [PMC free article] [PubMed] [Google Scholar]
- WANG B, WANG Z, FENG W, WANG M, HU Z, CHAI Z, ZHAO Y. New methods for nanotoxicology: synchrotron radiation-based techniques. Anal Bioanal Chem. 2010;398:667–76. doi: 10.1007/s00216-010-3752-2. [DOI] [PubMed] [Google Scholar]
- WEGNER K, P S. Scale-up of Nanoparticle Synthesis in Diffusion Flame Reactors. Chemical Engineering Science. 2003;58(20):4581–4589. [Google Scholar]
- WEST JB. Respiratory Physiology: The Essentials. Lippincott Williams & Wilkins; Philadelphia, PA: 2008. [Google Scholar]
- 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. 2008a;2:2121–34. doi: 10.1021/nn800511k. [DOI] [PMC free article] [PubMed] [Google Scholar]
- XIA T, KOVOCHICH M, LIONG M, ZINK JI, NEL AE. Cationic polystyrene nanosphere toxicity depends on cell-specific endocytic and mitochondrial injury pathways. ACS Nano. 2008b;2:85–96. doi: 10.1021/nn700256c. [DOI] [PubMed] [Google Scholar]
- YACOBI NR, MALMSTADT N, FAZLOLLAHI F, DEMAIO L, MARCHELLETTA R, HAMM-ALVAREZ SF, BOROK Z, KIM KJ, CRANDALL ED. Mechanisms of alveolar epithelial translocation of a defined population of nanoparticles. Am J Respir Cell Mol Biol. 2010;42:604–14. doi: 10.1165/rcmb.2009-0138OC. [DOI] [PMC free article] [PubMed] [Google Scholar]
- YANG S, SONG C, QIU T, GUO L, LI X. Synthesis of polystyrene/polysilsesquioxane core/shell composite particles via emulsion polymerization in the existence of poly(gamma-methacryloxypropyl trimethoxysilane) sol. Langmuir. 2013;29:92–101. doi: 10.1021/la303813q. [DOI] [PubMed] [Google Scholar]
- YE P, NADKARNI MA, SIMONIAN M, HUNTER N. CD24 regulated gene expression and distribution of tight junction proteins is associated with altered barrier function in oral epithelial monolayers. BMC Cell Biol. 2009;10 doi: 10.1186/1471-2121-10-2. doi: 10.1186/1471-2121-10-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- YEH TK, CHEN JK, LIN CH, YANG MH, YANG CS, CHOU FI, PEIR JJ, WANG MY, CHANG WH, TSAI MH, TSAI HT, LIN P. Kinetics and tissue distribution of neutron-activated zinc oxide nanoparticles and zinc nitrate in mice: effects of size and particulate nature. Nanotechnology. 2012;23 doi: 10.1088/0957-4484/23/8/085102. doi: 10.1088/0957-4484/23/8/085102. [DOI] [PubMed] [Google Scholar]
- ZHANG H, JI Z, XIA T, MENG H, LOW-KAM C, LIU R, POKHREL S, LIN S, WANG X, LIAO YP, WANG M, LI L, RALLO R, DAMOISEAUX R, TELESCA D, MADLER L, COHEN Y, ZINK JI, NEL AE. Use of metal oxide nanoparticle band gap to develop a predictive paradigm for oxidative stress and acute pulmonary inflammation. ACS Nano. 2012;6:4349–68. doi: 10.1021/nn3010087. [DOI] [PMC free article] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.






