A 3-dimensional in vitro model of epithelioid granulomas induced by high aspect ratio nanomaterials
© Sanchez et al; licensee BioMed Central Ltd. 2011
Received: 10 December 2010
Accepted: 18 May 2011
Published: 18 May 2011
The most common causes of granulomatous inflammation are persistent pathogens and poorly-degradable irritating materials. A characteristic pathological reaction to intratracheal instillation, pharyngeal aspiration, or inhalation of carbon nanotubes is formation of epithelioid granulomas accompanied by interstitial fibrosis in the lungs. In the mesothelium, a similar response is induced by high aspect ratio nanomaterials, including asbestos fibers, following intraperitoneal injection. This asbestos-like behaviour of some engineered nanomaterials is a concern for their potential adverse health effects in the lungs and mesothelium. We hypothesize that high aspect ratio nanomaterials will induce epithelioid granulomas in nonadherent macrophages in 3D cultures.
Carbon black particles (Printex 90) and crocidolite asbestos fibers were used as well-characterized reference materials and compared with three commercial samples of multiwalled carbon nanotubes (MWCNTs). Doses were identified in 2D and 3D cultures in order to minimize acute toxicity and to reflect realistic occupational exposures in humans and in previous inhalation studies in rodents. Under serum-free conditions, exposure of nonadherent primary murine bone marrow-derived macrophages to 0.5 μg/ml (0.38 μg/cm2) of crocidolite asbestos fibers or MWCNTs, but not carbon black, induced macrophage differentiation into epithelioid cells and formation of stable aggregates with the characteristic morphology of granulomas. Formation of multinucleated giant cells was also induced by asbestos fibers or MWCNTs in this 3D in vitro model. After 7-14 days, macrophages exposed to high aspect ratio nanomaterials co-expressed proinflammatory (M1) as well as profibrotic (M2) phenotypic markers.
Induction of epithelioid granulomas appears to correlate with high aspect ratio and complex 3D structure of carbon nanotubes, not with their iron content or surface area. This model offers a time- and cost-effective platform to evaluate the potential of engineered high aspect ratio nanomaterials, including carbon nanotubes, nanofibers, nanorods and metallic nanowires, to induce granulomas following inhalation.
Carbon nanotubes (CNTs) are a commercial success of nanotechnology with an expanding global market and potential applications for biomedical devices, imaging, drug delivery, tumor targeting, electronics, composite materials and sensing applications . The continued economic success of this industry is threatened by uncertainty and controversy surrounding potential adverse environmental and human health effects of engineered nanomaterials .
CNTs have been shown to induce significant toxicity using in vitro cellular assays and several in vivo rodent bioassays . In rodent bioassays using intratracheal instillation  or pharyngeal aspiration , multiwalled carbon nanotubes (MWCNTs) produced significant lung injury, epithelioid granulomas, and persistent interstitial inflammation and fibrosis. Granulomas are aggregates of epithelioid macrophages elicited by biopersistent irritants or microorganisms that are not killed during the acute inflammatory response . Two major types of granulomas are non-immune or foreign body granulomas (FBG) and antigenic or immunologic granulomas [6, 7]. Foreign body granulomas are characterized by aggregated epithelioid macrophages and multinucleated giant cells . If the stimulus is biopersistent, granulomas may persist for months or years and lead to tissue destruction and fibrosis .
A major controversy in nanotoxicology is whether the observed induction of lung inflammation and fibrosis following the bolus delivery of MWCNTs by intratracheal instillation or pharyngeal aspiration is an artifact associated with agglomeration of the carbon nanotubes prior to administration [5, 9]. However, a recent inhalation study  and a pharyngeal aspiration study using commercial samples of well-dispersed MWCNTs also induced significant lung inflammation characterized by multifocal granulomas . The specific physicochemical properties of carbon nanotubes responsible for lung toxicity are unknown. It is uncertain whether these pathologic responses are due to bioavailable metal catalyst residues, graphitic or amorphous carbon residues, length, geometry, high surface area, three-dimensional structure, agglomeration state, or some unique property of the carbon nanotube graphenic surface [12, 13].
There are numerous animal models of immune-mediated granulomas. In vitro models of immune-mediated granulomas have been induced by exposure of macrophages to pathogens or pathogen-coated beads. Macrophages exposed to heat-killed Candida albicans , Mycobacterium sp. , parasites such as Nippostrongylus brasiliensis , or antigens from Schistosoma sp. eggs bounded to 45 μm latex beads , produce granulomas in vitro.
Although non-degradable particles such as latex or dextran beads can induce foreign body or non-immune granulomas in monolayer cultures of macrophages , there is no in vitro model that recreates granuloma formation induced by biopersistent, high aspect ratio nanomaterials. To comply with a mandate issued by the U.S. National Academy of Sciences to replace animal testing with high-throughput in vitro cellular assays based on mechanistic pathways , we have developed a novel in vitro granuloma model. In this model, murine bone marrow-derived macrophages (BMDM) are cultured in a chemically-defined, serum-free medium as 3-dimensional spheroids in agarose wells. Cells maintain viability and macrophage phenotypic characteristics when exposed to sub-lethal doses of particulates up to14 days. Validation of this model for granuloma formation was done using carbon black particles (Printex 90) and crocidolite asbestos fibers as negative and positive reference materials, respectively, as recommended by an ILSI Working Group . Three commercial types of MWCNTs were tested for their ability to induce granuloma formation using this in vitro 3D model. Induction of granuloma formation was evaluated by formation of stable cellular aggregates, analysis of morphological changes characteristic of epithelioid macrophages, and activation phenotype of macrophages in response to high aspect ratio nanomaterials.
Characterization of reference and sample materials
Summary of material characterization
Surface area (m2/g)
141 ± 0.9(1)
2.8 ± 2.6 (1)(2)
116 ± 112(1)(2)
6.1 ± 2.5(1)
163 ± 49(1)
18.8 ± 7.4(1)
69 ± 30(1)
11.7 ± 3.6(1)(4)
80 ± 18(1)(4)
Determination of sub-lethal dose
Potential of high aspect ratio nanoparticles to induce granulomas
In 3D cultures, formation of cellular aggregates in response to asbestos fibers or MWCNT 1 and 2 was found to be dose-dependent. When treated at 0.05 μg/ml, macrophages form aggregates after 10 days (Additional file 1). When exposed to 0.5 μg/ml of asbestos fibers, cellular aggregates form after 3 days (Figure 4) and MWCNT 1 and 2 induced stable aggregates after 7 days (Additional file 1). Exposure to 0.05 or 0.5 μg/ml of MWCNT 3 induced aggregation after 3 days (Additional file 1). Exposure to carbon black did not induce cellular aggregation at any dose or time. In 2D cultures, untreated cells or cells exposed to 0.05 μg/ml (data not shown) or 0.5 μg/ml (Figure 4) of particulates showed formation of multinucleated giant cells. This effect may be due to prolonged attachment to a non-degradable surface in the presence of serum proteins as described previously [20, 21].
Morphological characteristics of in vitro granulomas
Untreated cells and cells exposed to carbon black particles show abundant cytoplasm, nuclei with an open chromatin pattern, prominent nucleoli, intact mitochondria, and short surface microvilli (Figure 5A and 5B). In contrast, asbestos fibers or MWCNTs induced well-formed, compact macrophage aggregates with ultrastructural features of epithelioid macrophages (Figure 5A). Most prominent is the extensive interdigitation of elongated, arborized surface microvilli. Particulates are contained in cytoplasmic membrane-bound vesicles with occasional free particulates observed in the cytoplasm (Figure 5B). Epithelioid macrophages contain abundant endoplasmic reticulum and large cytoplasmic vacuoles (Figure 5B) that are also characteristic of granulomas [22, 23].
Phagocytosis of high aspect ratio nanomaterials by macrophages in 3D cultures
Cellular activation in 3D cultures in response to particulates
Following exposure to microorganisms, macrophages undergo classical activation (M1 or pro-inflammatory phenotype) or differentiation towards alternatively activated macrophages (M2 or pro-fibrotic phenotype) [24–26]. Prototypical markers of the M1 phenotype include proinflammatory mediators including TNF-α, IL-1β, and IL-6 , and up-regulated iNOS expression . The anti-inflammatory or profibrotic M2 phenotype is characterized by induction of arginase-1 (Arg-1) and increased synthesis and release of mannose receptor (MR/CD206) .
First, we determined the ability of 2D and 3D cultures of macrophages to express a pro- or anti-inflammatory response by exposure to 100 ng/ml of lipopolysaccharide (LPS) or 20 ng/ml of IL-4 and IL-13, respectively (Additional file 2). LPS induced TNF-α release, iNOS expression, and decreased MR expression (Additional file 2 Figure S1). IL-4 or IL-13 induced Arg-1 expression, as well as expression and release of both MR and YM-1 (Additional file 2 Figure S2).
Although the ability of macrophages to respond towards a pro- or anti-inflammatory stimulus under 2D or 3D conditions is not impaired, we were unable to detect significant differences in the levels of these inflammatory mediators using ELISA (TNF-α) or Western blot assays (iNOS and Arg-1) when macrophages were exposed to 0.5 μg/ml of particulates compared to untreated cells. Additionally, no significant differences in IL-1β release were detected following exposure to these reference and test particulate materials at the sublethal doses used in these experiments in the absence of priming by LPS or phorbol ester (Additional file 3).
Compared to untreated cells, exposure to asbestos or MWCNTs induced an early increase in TNF-α expression and decreased expression of MR between 1 and 3 days. After day 7, this activation phenotype changes with variable TNF-α expression and increased MR expression following exposure to all particulates (Figure 7).
Exposure to asbestos or MWCNTs in 3D cultures also induces early iNOS expression after 3 - 7 days, followed by a progressive increase in Arg-1 expression (Figure 8). Induction of both iNOS and Arg-1 in untreated cells or cells exposed to carbon black was also evident at later time points but to a lesser extent than asbestos or MWCNT-treated cells (Figure 8). Phenotypic heterogeneity is evident following all exposures. The kinetics of expression of different phenotypic markers is not identical for all markers evaluated: TNF-α expression is upregulated prior to increased MR expression and no co-localization of these markers is observed (Figure 7). In contrast, iNOS expression increases early and is prolonged with a gradual transition to increasing Arg-1 co-expression between 7-14 days. Untreated cells or cells exposed to carbon black showed low levels of Arg-1 expression (Figure 8). This phenotypic heterogeneity and co-expression of M1 and M2 markers by a subset of macrophages following exposure to asbestos or MWCNTs is similar to the complex phenotype shown by murine macrophages isolated from healing wounds .
Particulate agglomeration before and after exposure
This in vitro model of granuloma formation uses murine BMDM differentiated in vitro using macrophage colony stimulation factor (M-CSF) (Additional file 4 Table S1) The phenotype of these differentiated cells resembles mature circulating blood monocytes (Additional file 4 Figure S1). These cells are recruited into the lungs  or the peritoneal cavity  in response to particulate stimuli following an early influx of neutrophils. If the particulate stimulus is toxic and biopersistent, these elicited macrophages may further differentiate into epithelioid macrophages and form a granuloma [22, 23]. Activation of BMDM and formation of stable aggregates with the morphological features of a foreign body or non-immune granuloma are successfully reproduced in this serum-free, in vitro model only in response to high aspect ratio nanomaterials, not to spherical carbon black particles that have chemically similar surfaces, also composed of sp2-hybridized (graphenic) carbon.
The relative ranking of these materials for induction of granulomas in this 3D models is: MWCNT 3 > asbestos > MWCNT 1, MWCNT 2 > carbon back. Surface area is not a major determinant of granuloma formation in this data set because the MWCNT 2 with a surface area of 200 m2/g did induce granuloma formation while carbon black nanoparticles with a surface area of 300 m2/g did not.
During in vitro exposure in this 3D model, all of the nanomaterials underwent agglomeration (Figure 9), especially MWCNT 3 as illustrated in Figure 10. This phenomenon may be driven by several events leading to entangled fibrous agglomerates that persist after the cells are lysed. First, internalization of materials may lead to intracellular aggregation during phagocytosis. Second, over time, macrophages may undergo repeated cycles of phagocytosis and cell death, resulting in extracellular release and accumulation of agglomerated fibrous nanomaterials.
High aspect ratio nanoparticles also induce frustrated phagocytosis and formation of multinucleated giant cells similar to the response of macrophages to asbestos fibers or carbon nanotubes following pharyngeal aspiration  or intraperitoneal or pleural injection [35, 36]. Similar to the study by Poland et al. , this in vitro model used a range of commercial MWCNT samples with an iron content of < 0.1 - 1.8 wt-%; however, these samples induced granulomas to the same extent as crocidolite asbestos, the positive reference sample, with an iron content of 22%. Porter et al.  used the same MWCNT as our sample 3 and did not detect generation of hydroxyl radical using electron spin resonance (ESR). Although redox activity of commercial carbon nanotubes is lower than that of amphibole asbestos fibers , this does not rule out a role for secondary generation of ROS by macrophages during phagocytosis of high aspect ratio nanomaterials .
The phenotype of BMDM induced by exposure of 3D cultures to asbestos fibers or MWCNTs also recapitulates the proinflammatory response of macrophages following inhalation of asbestos fibers. For example, inhalation of chrysotile or crocidolite asbestos by rats increased formation of nitrotyrosine in alveolar macrophages and other target cells of the lungs and pleura  suggesting induction of iNOS similar to this in vitro model. Asbestos fibers delivered by inhalation to the lungs  or by intraperitoneal injection to the mesothelium  elicit an acute inflammatory response due to the proinflammatory mediators produced by resident macrophages . Intratracheal instillation of asbestos fibers or MWCNTs in rats stimulated TNF-α release relative to ultrafine carbon black particles . In this in vitro model, asbestos fibers and MWCNTs also upregulated TNF-α protein expression in comparison to carbon black three days after exposure (Figure 7).
The proinflammatory mediators TNF-α, IL-1β, and iNOS have also been observed during the formation of immune granulomas in vivo  and in vitro . Less is known about the mediators involved in production and healing of non-immune granulomas. Non-immune or foreign body granulomas in the lung may progress to local fibrosis  similar to the reaction to well-dispersed MWCNTs delivered to the lungs of rodents by pharyngeal aspiration . The phenotype of activated macrophages in non-immune granulomas has not been characterized; however, arginase-1, a marker of M2 macrophage activation, is induced after 10-14 days following exposure to asbestos or MWCNTs in this in vitro model (Figure 8). Induction of arginase-1 is associated with a profibrotic phenotype  and may be useful as a biomarker to predict potential fibrosis induced by high aspect ratio nanoparticles. Co-expression of proinflammatory as well as profibrotic phenotypic markers by epithelioid macrophages may be responsible for sustained inflammation and rapid development of fibrosis induced by MWCNTs in the lungs of rodents [4, 11].
The biological mechanisms responsible for formation of stable aggregates of macrophages elicited from circulating blood monocytes in non-immune granulomas are unknown . Differentiation of monocytes into epithelioid macrophages is a morphological feature of granulomas. Epithelioid cells are large cells characterized by abundant endoplasmic reticulum, mitochondria, lysosomes, and cytoplasmic vesicles and vacuoles . Interdigititation of long, surface microvilli may be responsible for stable adhesion of epithelioid cells and they are the ultrastructural hallmark of granulomas ; these morphological features are produced by exposure to asbestos fibers or MWCNTs, but not to carbon black (Figure 4). The complex 3D aggregate structure (Figure 1C) characteristic of these commercial carbon nanotube samples may promote macrophage aggregation and granuloma formation in vitro and in vivo.
A major caveat in in vitro nanotoxicology assays is the high dose delivered to target cells that may not reflect human exposure under realistic conditions . In this in vitro model, 1.4 × 105 BMDM were exposed to 0.05-0.5 μg of test particulates. Elder et al.  established a subchronic NOAEL for Printex 90, the carbon black sample used in this in vitro study, and determined that approximately 0.1 mg was deposited in the lungs of rats after 13 weeks inhalation at a dose of 1 mg/m3. Assuming 3 × 107 alveolar macrophages per rat [47, 48], the dose used in this in vitro assay is close to the deposited dose of carbon black under conditions that do not induce impaired clearance or inflammation. For comparison, airborne dust levels of MWCNTs measured by Han et al.  in a research facility were 400 μg/m3 and this dose corresponded to the doses delivered to mice by pharyngeal aspiration that produced lung granulomas and diffuse interstitial fibrosis .
The distinctive morphological and phenotypic responses of BMDM to reference particulates and MWCNTs in serum-free 3D culture establish proof-of-principle for this in vitro model as a potential alternative to both traditional 2D monolayer cultures and to rodent bioassays for granuloma formation. This in vitro 3D model is a promising platform for testing of various commercial varieties of carbon nanotubes as well as other new high aspect ratio or one-dimensional nanomaterials including metallic nanowires , and ZnO or TiO2 nanorods and nanobelts 
Materials and methods
Isolation and culture of bone marrow-derived macrophages
This protocol was approved by the Brown University Institutional Animal Care and Use Committee in accordance with the Animal Welfare Act and the National Institute of Health Guide for the Care and Use of Laboratory Animals. Murine bone marrow-derived macrophages were differentiated from bone marrow cells isolated from 6- to 8- week-old C57BL/6J male mice (Jackson Laboratories, Bar Harbor, ME). Briefly, animals were sacrificed by CO2 asphyxiation, femurs were removed, and bone marrow was harvested by flushing with 3 ml of Dulbecco's Modified Eagle medium (DMEM; Invitrogen, Carlsbad, CA) supplemented with 20% fetal bovine serum (FBS; Atlanta Biologicals, Lawrenceville, GA), 10 units/ml penicillin, and 10 μg/ml of streptomycin (Invitrogen, Carlsbad, CA). Cells were collected in a 50 ml conical tube on ice, centrifuged at 500 g for 5 min at 4°C. Cells were resuspended in fresh media supplemented with 20 ng/ml of M-CSF (R&D Systems, Minneapolis, MA) and incubated overnight at 37°C in a humidified atmosphere of 5% CO2. Non-adherent cells were harvested and transferred to 10 cm non-tissue culture-treated polystyrene dishes. After 3 days the medium was replaced with fresh medium and, on day 7, non-adherent cells were removed. Adherent cells were washed 5 times with PBS, and 10 ml of serum-free medium (SFM) was added to each dish: X-Vivo 15 medium supplemented with 1X HL-1 (Lonza Rockland Inc., Rockland, ME), 20 ng/ml M-CSF and 10 units/ml penicillin and 10 μg/ml of streptomycin. On day 10, cells were detached with 5 mM of EDTA, centrifuged at 500 g for 5 min at 4°C, resuspended, and plated in SFM at 0.14 × 106 cells/ml. A 200 μl volume of cell suspension (35,000 cells) was added to each well of a 96-well microplate. For three dimensional cultures, wells were previously coated with 50 μl of 3% (wt/vol) low melting point agarose (SeamPlaque, Lonza Rockland Inc.) dissolved by boiling in endotoxin-free water (Sigma-Aldrich, St. Louis, MO). Coated wells were equilibrated with SFM for 24 hrs at 37°C and 5% CO2 in humidified chamber prior to use. In order to avoid endotoxin contamination, glassware and plastic containers were washed with PyroCLEAN™ detergent (AlerCHEK, Portland, ME) and autoclaved before use. Cells were kept up to 14 days and 2/5 of medium was replaced with fresh medium every other day. Light microscopy did not reveal any contamination with fibroblasts after 14 days.
Materials and cell treatments
Crocidolite asbestos fiber stocks ranging from 0.1 to 35 μm in length and 30 to 3000 nm in diameter, originally characterized by the International Union Against Cancer (UICC, Timbrell, 1971/72), were purchased from Duke Scientific (Palo Alto, CA). Carbon black particles (Printex-90, Evonik, Essen, Germany) with an average primary particle size of 14 nm and MWCNT 3 produced by chemical vapor deposition (CVD) with average dimension of 13 μm in length and 85 nm in diameter (MWCNT 3, MWCNT-7, Mitsui & Co. Ltd; Tsukuba, Ibaraki, Japan) were a gift of Dr. Günter Oberdörster (University of Rochester, Rochester, NY). MWCNT 1 (mean length 7 ± 2 μm, mean diameter 140 ± 30 nm) and MWCNT 2 (mean length 30 μm, mean diameter 35 ± 10 nm) produced by CVD were purchased from MER Corporation (Tucson, AZ). Size distribution of MWCNTs in serum-free medium was evaluated by SEM and TEM using NIH Image/ImageJ software (Table 1).
Asbestos fibers were baked in an oven at 250°C for 16 hrs to remove endotoxin. Stocks at 0.5 mg/ml in endotoxin free water (Sigma) were autoclaved and stored at 4°C. This sterilization protocol did not decrease the biological activity of asbestos fibers following intraperitoneal injection in mice  or redox activity as assessed by plasmid DNA break assay . Removal of endotoxin and sterilization of carbon nanomaterials were done by heating at 400°C for 30 min in a furnace under continuous flow of nitrogen gas to prevent oxidation.
Stocks at 0.5 mg/ml in sterile endotoxin free water were stored at 4°C. Working solutions were prepared by dilution of stock suspensions in SFM. Briefly, stock suspensions were water-bath sonicated for a minimum of 30 min using a tabletop ultrasonic water bath (Branson Ultrasonic Corporation, Danbury, CT). After 30 min, the sample was mixed by pipeting up and down during sonication and 1 ml of the stock was transferred to a clean tube using wide bore, low retention tips (Axygen INC, Union City, CA), then brought to the desired concentration with SFM and sonicated for an additional 5 minutes. A volume of 50 μl of working solution was added to each well at a final volume of 250 μl. Dry materials and suspensions were handled under a Class IIB laminar flow hood equipped with Hepa filters with external exhaust. Endotoxin levels of the stock suspensions were less than 0.24 EU/ml as determined by gel-clot assay (Embryotch™ Laboratories, Wilmington, MA).
Determination of cell viability
Total DNA content was used as an indicator of total cell number. At the specified time, culture medium was removed and cells were digested with fungal proteinase K (Invitrogen) at a final concentration of 50 μg/ml (≥ 1 unit/ml) in TE buffer (200 mM Tris-Cl, 20 mM EDTA, pH 7.5) overnight at 37°C and stored at -20°C until use. Digested cell suspensions were brought to 300 μl of final volume with TE buffer and a 20 μl aliquot was used to determine DNA content. Double-stranded DNA was quantified using Quant-it Picogreen dsDNA kit (Molecular Probes, Eugene, OR) following the manufacturer's protocol for a 200 μl reaction assay. Briefly, samples were diluted with TE buffer to a final volume of 100 μl and 100 μl of the Quant-it Picogreen working solution was added to each sample, mixed, and incubated for 5 min at room temperature protected from light. Samples were excited at 480 nm and fluorescence emission intensity was measured at 520 nm using a fluorescence microplate reader (SpectraMax M2, Molecular Devices, Sunnyvale, CA). Under these conditions, the linear detection range of the assay was used for all treatments and no interference due to test particulates was observed.
For intracellular staining of TNF-α and mannose receptor (MR), cells were pre-incubated with Brefeldin A (BD Biosciences, Franklin Lakes, NJ) for 6 hrs prior to fixation. Cells were fixed in 4% paraformaldehyde in PBS for 30 min at room temperature, washed 3 times with 0.1% BSA/PBS, and permeabilized in 0.25% (w/v) saponin/blocking solution for 10 min. After washing, cells were incubated for 30 min in blocking solution. Following incubation overnight at 4°C with primary antibodies against arginase-1, iNOS, TNF-α (BD Biosciences) or MR (AbD Serotec, Oxford, UK) in blocking solution, cells were washed with PBS and incubated with secondary antibodies in blocking solution for 2 hrs at room temperature. After three washes with PBS, cells were mounted on glass slides using Vectashield (Vector Lab. Inc., Burlingame, CA) with DAPI as a nuclear counterstain. Samples were analyzed using SlideBook software (Intelligent Imagine Innovations, Denver, CO) and spinning disk confocal scanning microscopy (Olympus IX81, Olympus Corporation, Tokyo, Japan) using appropriate filters for dual wavelength immunofluorescence.
Bone marrow-derived macrophages in agarose-coated wells were transferred to glass LabTek wells (Nunc, Thermo Fisher Scientific Inc. Rochester, NY) and incubated for 6 to 24 hrs to allow cell attachment and spreading. Attached cells were fixed with methanol pre-chilled to -20°C. Slides were immersed for 3 min in filtered May-Grünwald (Sigma) and 2 min in Giemsa (Sigma) followed by 30 sec in acetone, 2:1 acetone: xylene, 1:2 acetone: xylene and xylene. Slides were air-dried and mounted with Permount™ Mounting Media (Fisher, Pittsburgh, PA). Light micrographs were taken using a Nikon Eclipse 501 (Nikon Instruments Inc, Melville, NY) microscope. Images were acquired and analyzed with SOPT Insight FireWire imaging software (SPOT Imaging Solutions, Sterling Heights, MI).
Toluidine blue stain
Macrophages in 3D cultures were fixed as pellets at room temperature for 30 min in 2% glutaraldehyde in 0.1 M sodium cacodylate buffer, pH 7.4, rinsed, and stored at 4°C in 0.1 M sodium cacodylate buffer with 8% sucrose for further processing. Cells were post-fixed with 1% osmium tetroxide in 0.1 M sodium cacodylate buffer for 30 min at room temperature and rinsed 3 times with buffer for 5 min. Following dehydration in graded ethanols (70%, 90% and 95%) for 10 min and 3 changes of 100% ethanol for 5 min, samples were infiltrated for 12-18 hours in a 1:1 mixture of 100% ethanol and embedding resin (Spurr Low Viscosity Embedding Medium, Electron Microscopy Sciences, Hatfield, PA). Samples were placed in 100% embedding media for 4 hours, and placed in a mold with fresh resin. Blocks were polymerized in an oven at 65°C overnight and sectioned on a Reichert Ultracut Ultramicrotome at a thickness of 0.5 μm using a diamond knife (Diatome US, Hatfield, PA). Following toluidine blue stain, slides were air dried and mounted in Permount™ Mounting Media (Fisher). Light micrographs were taken using a Nikon Eclipse 501 microscope (Nikon Instruments Inc, Melville, NY) and SOPT Insight FireWire software.
Transmission Electron Microscopy
90 nm sections from the same plastic-embedded block used for toluidine blue stain were stained with 1% uranyl acetate in 50% methanol for 10 min and lead citrate for 5 min, placed on copper grids, and viewed with a Phillips 410 Transmission Electron Microscope equipped with an Advantage HR CCD camera (Advanced Microscopy Techniques, Danvers, MA). Images were acquired and analyzed with AMT's imaging software.
Scanning electron microscopy (SEM)
Morphological analysis of materials prior to exposure
Materials were dispersed in serum-free medium at different concentrations, followed by water-bath (Branson Ultrasonic Corporation) sonication for 30 min and vacuum filtered through a PVCD membrane (Millipore, Billerica, MA).
Morphological analysis of materials post-exposure
After 14 days of exposure, cells from 3D cultures were collected, washed, and resuspended in lysis buffer (2% Triton X-100, 10 mM Tris-HCl, pH 8, 150 mM NaCl, 10 mM NaN3, 10 mM EDTA, 5 mM iodoacetamide, 2 mM phenylmethylsulfonyl fluoride, 1 g/ml pepstatin, and 1 M leupeptin). After incubation for 30 min on ice and vortexing every 10 min, cell lysates were centrifuged at 10,000 × g for 10 min at 4°C in a Sorvall Legend Mach 1.6 R centrifuge (Kendro Laboratory Products Inc, Asheville, NC). Supernatants were discarded, pellets were resuspended in 50 ml of methanol, followed by water-bath sonication for 1 hr and vacuum filtered through a PVCD membrane (Millipore).
Cellular phagocytosis and aggregation
After 0.5, 6, and 24 hrs of exposure to 1.25 μg/ml (1 μg/cm2) of asbestos fibers or MWCNTs, cells in 3D cultures were transferred to a glass coverslip, incubated for 15 min to allow attachment and fixed with 2.5% gluteraldehyde in 0.1 M cacodylate buffer.
All images were taken using a LEO 1530 Thermally-Assisted Field Emission (TFE) Scanning Electron Microscope (SEM) (LEO, Germany).
Data were analyzed using MatLab software (MathWorks, Natick, MA). All results are presented as the mean ± standard deviation (SD). Differences were compared by Scheffé's method after analysis of variance (ANOVA). A p value < 0.05 was considered as statistically significant.
This work was supported by the National Institute of Environmental Health Sciences at the National Institutes of Health (Superfund Research Program P42 ES013660 , R01 ES016178, and T32 E07272).
We would like to thank Professor Jeffrey Morgan for helpful discussions about 3D cell culture models.
- Madl AK, Pinkerton KE: Health effects of inhaled engineered and incidental nanoparticles. Crit Rev Toxicol 2009, 39: 629–658. 10.1080/10408440903133788PubMedView ArticleGoogle Scholar
- Stern ST, McNeil SE: Nanotechnology safety concerns revisited. Toxicol Sci 2008, 101: 4–21.PubMedView ArticleGoogle Scholar
- Donaldson K, Aitken R, Tran L, Stone V, Duffin R, Forrest G, Alexander A: Carbon nanotubes: a review of their properties in relation to pulmonary toxicology and workplace safety. Toxicol Sci 2006, 92: 5–22. 10.1093/toxsci/kfj130PubMedView ArticleGoogle Scholar
- 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.PubMedView ArticleGoogle Scholar
- Porter AE, Gass M, Bendall JS, Muller K, Goode A, Skepper JN, Midgley PA, Welland M: Uptake of noncytotoxic acid-treated single-walled carbon nanotubes into the cytoplasm of human macrophage cells. ACS Nano 2009, 3: 1485–1492. 10.1021/nn900416zPubMedView ArticleGoogle Scholar
- Majno G, Joris I: Cells, tissues, and disease: principles of general pathology. 2nd edition. New York: Oxford University Press; 2004.Google Scholar
- Kunkel SL, Lukacs NW, Strieter RM, Chensue SW: Animal models of granulomatous inflammation. Semin Respir Infect 1998, 13: 221–228.PubMedGoogle Scholar
- Mukhopadhyay S, Gal AA: Granulomatous lung disease, an approach to differental diagnosis. Arch Pathol Lab Med 2010, 134: 667–690.PubMedGoogle Scholar
- Warheit DB: Long-term inhalation toxicity studies with multiwalled carbon nanotubes: closing the gaps or initiating the debate? Toxicol Sci 2009, 112: 273–275. 10.1093/toxsci/kfp237PubMedView ArticleGoogle Scholar
- Ma-Hock L, Treumann S, Strauss V, Brill S, Luizi F, Mertler M, Wiench K, Gamer AO, van Ravenzwaay B, Landsiedel R: Inhalation toxicity of multiwall carbon nanotubes in rats exposed for 3 months. Toxicol Sci 2009, 112: 468–481. 10.1093/toxsci/kfp146PubMedView ArticleGoogle Scholar
- 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.2009.10.017PubMedView ArticleGoogle Scholar
- Donaldson K: Resolving the nanoparticles paradox. Nanomedicine (Lond) 2006, 1: 229–234. 10.2217/174358184.108.40.206View ArticleGoogle Scholar
- Sanchez VC, Pietruska JR, Miselis NR, Hurt RH, Kane AB: Biopersistence and potential adverse health impacts of fibrous nanomaterials: what have we learned from asbestos? Wiley Interdiscip Rev Nanomed Nanobiotechnol 2009, 1: 511–529. 10.1002/wnan.41PubMed CentralPubMedView ArticleGoogle Scholar
- Heinemann DE, Peters JH, Gahr M: A human in vitro granuloma model using heat killed Candida albicans cells immobilized on plastic culture wells. Scand J Immunol 1997, 45: 596–604. 10.1046/j.1365-3083.1997.d01-435.xPubMedView ArticleGoogle Scholar
- Puissegur MP, Botanch C, Duteyrat JL, Delsol G, Caratero C, Altare F: An in vitro dual model of mycobacterial granulomas to investigate the molecular interactions between mycobacteria and human host cells. Cell Microbiol 2004, 6: 423–433. 10.1111/j.1462-5822.2004.00371.xPubMedView ArticleGoogle Scholar
- Seitzer U, Haas H, Gerdes J: A human in vitro granuloma model for the investigation of multinucleated giant cell and granuloma formation. Histol Histopathol 2001, 16: 645–653.PubMedGoogle Scholar
- Shikama Y, Kobayashi K, Kasahara K, Kaga S, Hashimoto M, Yoneya I, Hosoda S, Soejima K, Ide H, Takahashi T: Granuloma formation by artificial microparticles in vitro. Macrophages and monokines play a critical role in granuloma formation. Am J Pathol 1989, 134: 1189–1199.PubMed CentralPubMedGoogle Scholar
- NRC: Toxicity Testing in the 21st Century: A vision and a strategy. Washington, DC: National Academy Press; 2007.Google Scholar
- Oberdörster G, Maynard A, Donaldson K, Castranova V, Fitzpatrick J, Ausman K, Carter J, Karn B, Kreyling W, Lai D, Olin S, Monteiro-Riviere N, Warheit D, Yang H: Principles for characterizing the potential human health effects from exposure to nanomaterials: elements of a screening strategy. Part Fibre Toxicol 2005, 2: 8. 10.1186/1743-8977-2-8PubMed CentralPubMedView ArticleGoogle Scholar
- Collier TO, Thomas CH, Anderson JM, Healy KE: Surface chemistry control of monocyte and macrophage adhesion, morphology, and fusion. J Biomed Mater Res 2000, 49: 141–145. 10.1002/(SICI)1097-4636(200001)49:1<141::AID-JBM18>3.0.CO;2-APubMedView ArticleGoogle Scholar
- Jenney CR, Anderson JM: Adsorbed serum proteins responsible for surface dependent human macrophage behavior. J Biomed Mater Res 2000, 49: 435–447. 10.1002/(SICI)1097-4636(20000315)49:4<435::AID-JBM2>3.0.CO;2-YPubMedView ArticleGoogle Scholar
- Turk JL, Narayanan RB: The origin, morphology, and function of epithelioid cells. Immunobiology 1982, 161: 274–282.PubMedView ArticleGoogle Scholar
- Wang NS: Electron microscopy in diagnostic pathology. In Electron Microscopy of the Lung. Edited by: DE S. Marcel Deker, Inc New York; 1990:429–490.Google Scholar
- Gordon S, Martinez FO: Alternative activation of macrophages: mechanism and functions. Immunity 2010, 32: 593–604. 10.1016/j.immuni.2010.05.007PubMedView ArticleGoogle Scholar
- Gordon SB, Read RC: Macrophage defences against respiratory tract infections. Br Med Bull 2002, 61: 45–61. 10.1093/bmb/61.1.45PubMedView ArticleGoogle Scholar
- Martinez FO, Helming L, Gordon S: Alternative activation of macrophages: an immunologic functional perspective. Annu Rev Immunol 2009, 27: 451–483. 10.1146/annurev.immunol.021908.132532PubMedView ArticleGoogle Scholar
- Mantovani A, Sica A, Sozzani S, Allavena P, Vecchi A, Locati M: The chemokine system in diverse forms of macrophage activation and polarization. Trends Immunol 2004, 25: 677–686. 10.1016/j.it.2004.09.015PubMedView ArticleGoogle Scholar
- Jacobs AT, Ignarro LJ: Lipopolysaccharide-induced expression of interferon-beta mediates the timing of inducible nitric-oxide synthase induction in RAW 264.7 macrophages. J Biol Chem 2001, 276: 47950–47957.PubMedGoogle Scholar
- Daley JM, Brancato SK, Thomay AA, Reichner JS, Albina JE: The phenotype of murine wound macrophages. J Leukoc Biol 2009.Google Scholar
- Lehnert BE: Defense mechanisms against inhaled particles and associated particle-cell interactions. Rev in Mineraology 1993, 28: 427–469.Google Scholar
- Moalli PA, MacDonald JL, Goodglick LA, Kane AB: Acute injury and regeneration of the mesothelium in response to asbestos fibers. Am J Pathol 1987, 128: 426–445.PubMed CentralPubMedGoogle Scholar
- Lam CW, James JT, McCluskey R, Hunter RL: Pulmonary toxicity of single-wall carbon nanotubes in mice 7 and 90 days after intratracheal instillation. Toxicol Sci 2004, 77: 126–134.PubMedView ArticleGoogle Scholar
- Shvedova AA, Kisin E, Murray AR, Johnson VJ, Gorelik O, Arepalli S, Hubbs AF, Mercer RR, Keohavong P, Sussman N, Jin J, Yin J, Stone S, Chen BT, Deye G, Maynard A, Castranova V, Baron PA, Kagan VE: Inhalation vs. aspiration of single-walled carbon nanotubes in C57BL/6 mice: inflammation, fibrosis, oxidative stress, and mutagenesis. Am J Physiol Lung Cell Mol Physiol 2008, 295: L552–565. 10.1152/ajplung.90287.2008PubMed CentralPubMedView ArticleGoogle Scholar
- Porter D SK, Wolfarth M, Jefferson A, Schwegler-Berry D, Andrew ME, Castranova V: A biocompatible medium for nanoparticle dispersion. Nanotoxicology 2008, 2: 144–152. 10.1080/17435390802318349View ArticleGoogle Scholar
- Poland CA, Duffin R, Kinloch I, Maynard A, Wallace WA, Seaton A, Stone V, Brown S, Macnee W, Donaldson K: Carbon nanotubes introduced into the abdominal cavity of mice show asbestos-like pathogenicity in a pilot study. Nat Nanotechnol 2008, 3: 423–428. 10.1038/nnano.2008.111PubMedView ArticleGoogle Scholar
- Donaldson K, Murphy FA, Duffin R, Poland CA: Asbestos, carbon nanotubes and the pleural mesothelium: a review of the hypothesis regarding the role of long fibre retention in the parietal pleura, inflammation and mesothelioma. Part Fibre Toxicol 2010, 7: 5. 10.1186/1743-8977-7-5PubMed CentralPubMedView ArticleGoogle Scholar
- Guo LMD, Lui X, Vaslet C, Hurt RH, Kane AB: Iron bioavailability and redos activity in diverse carbon nanotubes samples. Chem Mater 2007, 19: 3472–3478. 10.1021/cm062691pView ArticleGoogle Scholar
- Tanaka S, Choe N, Hemenway DR, Zhu S, Matalon S, Kagan E: Asbestos inhalation induces reactive nitrogen species and nitrotyrosine formation in the lungs and pleura of the rat. J Clin Invest 1998, 102: 445–454. 10.1172/JCI3169PubMed CentralPubMedView ArticleGoogle Scholar
- Kagan E, Oghiso Y, Hartmann DP: Enhanced release of a chemoattractant for alveolar macrophages after asbestos inhalation. Am Rev Respir Dis 1983, 128: 680–687.PubMedGoogle Scholar
- Lukacs NW, Chensue SW, Strieter RM, Warmington K, Kunkel SL: Inflammatory granuloma formation is mediated by TNF-alpha-inducible intercellular adhesion molecule-1. J Immunol 1994, 152: 5883–5889.PubMedGoogle Scholar
- Seitzer U, Scheel-Toellner D, Toellner KM, Reiling N, Haas H, Galle J, Flad HD, Gerdes J: Properties of multinucleated giant cells in a new in vitro model for human granuloma formation. J Pathol 1997, 182: 99–105. 10.1002/(SICI)1096-9896(199705)182:1<99::AID-PATH807>3.0.CO;2-XPubMedView ArticleGoogle Scholar
- El-Zammar OA, Katzenstein AL: Pathological diagnosis of granulomatous lung disease: a review. Histopathology 2007, 50: 289–310. 10.1111/j.1365-2559.2006.02546.xPubMedView ArticleGoogle Scholar
- Wynn TA: Fibrotic disease and the T(H)1/T(H)2 paradigm. Nat Rev Immunol 2004, 4: 583–594. 10.1038/nri1412PubMed CentralPubMedView ArticleGoogle Scholar
- Majno GaJI: Cells, tissues, and disease: principles of general pathology. Oxford University; 2004:446–476.Google Scholar
- Oberdörster G: Safety assessment for nanotechnology and nanomedicine: concepts of nanotoxicology. J Intern Med 2010, 267: 89–105. 10.1111/j.1365-2796.2009.02187.xPubMedView ArticleGoogle Scholar
- Elder A, Gelein R, Finkelstein JN, Driscoll KE, Harkema J, Oberdörster G: Effects of subchronically inhaled carbon black in three species. I. Retention kinetics, lung inflammation, and histopathology. Toxicol Sci 2005, 88: 614–629. 10.1093/toxsci/kfi327PubMedView ArticleGoogle Scholar
- Tao F, Gonzalez-Flecha B, Kobzik L: Reactive oxygen species in pulmonary inflammation by ambient particulates. Free Radic Biol Med 2003, 35: 327–340. 10.1016/S0891-5849(03)00280-6PubMedView ArticleGoogle Scholar
- Oberdörster G, Yu CP: Lung dosimetry--considerations for noninhalation studies. Exp Lung Res 1999, 25: 1–6. 10.1080/019021499270385PubMedView ArticleGoogle Scholar
- Han JH, Lee EJ, Lee JH, So KP, Lee YH, Bae GN, Lee SB, Ji JH, Cho MH, Yu IJ: Monitoring multiwalled carbon nanotube exposure in carbon nanotube research facility. Inhal Toxicol 2008, 20: 741–749. 10.1080/08958370801942238PubMedView ArticleGoogle Scholar
- Hamilton RF, 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. 10.1186/1743-8977-6-35PubMed CentralPubMedView ArticleGoogle Scholar
This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.