Extrapulmonary transport of MWCNT following inhalation exposure
© Mercer et al.; licensee BioMed Central Ltd. 2013
Received: 9 April 2013
Accepted: 6 August 2013
Published: 9 August 2013
Inhalation exposure studies of mice were conducted to determine if multi-walled carbon nanotubes (MWCNT) distribute to the tracheobronchial lymphatics, parietal pleura, respiratory musculature and/or extrapulmonary organs. Male C57BL/6 J mice were exposed in a whole-body inhalation system to a 5 mg/m3 MWCNT aerosol for 5 hours/day for 12 days (4 times/week for 3 weeks, lung burden 28.1 ug/lung). At 1 day and 336 days after the 12 day exposure period, mice were anesthetized and lungs, lymph nodes and extrapulmonary tissues were preserved by whole body vascular perfusion of paraformaldehyde while the lungs were inflated with air. Separate, clean-air control groups were studied at 1 day and 336 days post-exposure. Sirius Red stained sections from lung, tracheobronchial lymph nodes, diaphragm, chest wall, heart, brain, kidney and liver were analyzed. Enhanced darkfield microscopy and morphometric methods were used to detect and count MWCNT in tissue sections. Counts in tissue sections were expressed as number of MWCNT per g of tissue and as a percentage of total lung burden (Mean ± S.E., N = 8 mice per group). MWCNT burden in tracheobronchial lymph nodes was determined separately based on the volume density in the lymph nodes relative to the volume density in the lungs. Field emission scanning electron microscopy (FESEM) was used to examine MWCNT structure in the various tissues.
Tracheobronchial lymph nodes were found to contain 1.08 and 7.34 percent of the lung burden at 1 day and 336 days post-exposure, respectively. Although agglomerates account for approximately 54% of lung burden, only singlet MWCNT were observed in the diaphragm, chest wall, liver, kidney, heart and brain. At one day post exposure, the average length of singlet MWCNT in liver and kidney, was comparable to that of singlet MWCNT in the lungs 8.2 ± 0.3 versus 7.5 ± 0.4 um, respectively. On average, there were 15,371 and 109,885 fibers per gram in liver, kidney, heart and brain at 1 day and 336 days post-exposure, respectively. The burden of singlet MWCNT in the lymph nodes, diaphragm, chest wall and extrapulmonary organs at 336 days post-exposure was significantly higher than at 1 day post-exposure.
Inhaled MWCNT, which deposit in the lungs, are transported to the parietal pleura, the respiratory musculature, liver, kidney, heart and brain in a singlet form and accumulate with time following exposure. The tracheobronchial lymph nodes contain high levels of MWCNT following exposure and further accumulate over nearly a year to levels that are a significant fraction of the lung burden 1 day post-exposure.
With the wide spread development of commercial carbon nanotube manufacturing and commercial application, carbon nanotubes (CNT) such as MWCNT are an important category of nanoparticle for health risk assessment. There is a need to address the associated bioactivity of these newly manufactured materials. Initial studies focused on the respiratory effects of pulmonary exposure but were limited by the lack of knowledge concerning the occupational levels. Ongoing studies of environments where worker exposure may occur are providing the necessary data to provide realistic inhalation exposures necessary for health risk assessments .
MWCNT aspiration exposures in mice conducted at lung burdens relevant to measured occupational exposures have demonstrated early dose- and time-dependent pulmonary inflammation and damage . MWCNT aerosol exposures have demonstrated a variety of effects such as thickening of the alveolar septa , severe airway fibrosis in sensitized mice , and diffuse histiocytic and neutrophilic inflammation with persistent pulmonary inflammation and granulomas .
The small size, lipophilic nature and reported occurrence in the visceral pleura and pleural space [2, 6–8] indicate that MWCNT may disseminate elsewhere in the body following pulmonary exposure. Interest in detection of this potential extrapulmonary transport has been increased by reports demonstrating extrapulmonary effects of CNT in the brain  and cardiovascular system [10–12] as well as demonstrations that CNT have genotoxic effects  and activate several carcinogenic-related signaling pathways .
Traditional studies of extrapulmonary transport have been based on detection of a tracer label, typically radioactive [15–17], fluorescent [18, 19] or a unique elemental form such as colloidal gold  which can be detected by inductively couple plasma mass spectrometry or neutron activation studies. The limits of detection for these methods are typically set either by the instability of the tracer label, instrument sensitivity or the elemental nature of the tracer. For instance, neutron activation analysis has detection limits ranging from a few micrograms per gram of tissue to nanogram levels [21, 22]. Detection limits by neutron activation depend on suitable elemental composition and are a function of the element and background interference. While potentially very sensitive, these methods do not generally allow microscopic visualization of individual particles or particle-tissue interactions.
Developments in microscope technology such as enhanced darkfield microscopy allow the direct detection and imaging of singlet CNT. Enhanced darkfield microscopy has been applied for detection and analysis of nanoparticles within the lungs from a variety of exposure [23–25]. We have recently applied enhanced darkfield microscopy techniques to detection of MWCNT in extrapulmonary organs following a 1 day inhalation exposure. That study demonstrated MWCNT translocation to extrapulmonary organs, detecting MWCNT in all the extrapulmonary organs sampled (liver, kidney and heart) within 24 hours of exposure  In this report, we extended those observations to a chronic post-exposure study to include a more extensive sampling of sites including the tracheobronchial lymph nodes, the diaphragm, chest wall and brain in addition to the liver, kidney and heart. In addition, we compared the distribution in these sites at 1 day and 336 days after the termination of exposure in order to determine if there was a significant accumulation of MWCNT in systemic tissue with time post-exposure.
Extrapulmonary MWCNT concentration, number
Day post-inhalation 1
Concentration #/gm tissue
% of lung burden 2
The light micrograph of the same singlet MWCNT on the left side of Figure 4 was only visible over a narrow range of focus and was very difficult to identify even though nearby cells, visible in enhanced darkfield imaging, were clearly visible in the light microscope. The exercise of identifying singlet MWCNT in lavage fluid from the pleural space, and the example of side-by-side comparison of enhanced darkfield versus light microscopy of MWCNT structures containing a few or singlet MWCNT structures indicate that enhanced darkfield is the optimal instrument for scanning of wide fields to detect nanoparticles. Based on side-by-side comparisons, the transmitted light microscope is not a reliable tool for identification of these MWCNT structures.
The high level of MWCNT burden delivered to the tracheobronchial lymph nodes was approximately 300 times greater than the burden delivered to the liver which was the highest observed in extra-pulmonary organs. Total MWCNT burden for diaphragm, chest wall and extrapulmonary organs was 0.009 and 0.037 percent of lung burden at 1 day and 336 days, respectively, after exposure. By 336 days post-exposure there was a 6 to 7-fold increase in the concentration of MWCNT in extrapulmonary organs and diaphragm, excluding the chest wall. MWCNT in the chest wall did not change significantly over this period.
The chest wall, which had a concentration of fibers comparable to that of the overall median concentration for extrapulmonary organs at 1 day post exposure did not accumulate fibers with time post-exposure as was observed for other organs. At the same time, the diaphragm, which is the other major pleural opposed surface, demonstrated an approximate 7-fold increase similar to the other organs examined. The chest wall, unlike other tissues, was decalcified prior to embedding and sectioning. This difference in treatment could be responsible. To test for a treatment effect, weighed samples of the MWCNT were treated extensively with the decalcification solution in the same manner as the chest wall tissue and then washed, dried and reweighed. In FESEM examination of the formic acid-treated MWCNT fibers, no apparent degradation due to the treatment was observed. Average length of MWCNT fibrils in the chest wall section was not significantly different than that of the diaphragm which was not decalcified with formic acid.
In Table 1 are given the organ weights, concentration of MWCNT fibers per gram of tissue, total MWCNT fibers in each tissue and the percentage relative to the lung burden at 1 day post-exposure for the tracheobronchial lymph nodes, diaphragm, chest wall and extrapulmonary organs. Excluding the lymph nodes and respiratory muscles, the concentrations at 1 day post-exposure varied by a factor of four with the highest concentration in the liver at 25,767 fibers/g and the lowest in the brain at 7,231 fibers/g. At 1 day post-exposure the order in terms of fibers per gram was liver, kidney, heart, and brain with the liver concentration being significantly elevated above the other organs. This does not appear to follow the order that is found in the distribution of blood flow per ml min-1 g-1 which has been reported to be heart, kidney, brain and liver based on radiolabeled microspheres in anesthetized mice . Enhanced uptake of MWCNT by the reticuloendothelial system of the liver, fenestrated endothelium of the kidney and restricted uptake due to the blood–brain-barrier in the brain may account for these differences between organ blood flow and MWCNT uptake.
Recent developments in microscope technology, such as enhanced darkfield microscopy, allow the direct detection and imaging of singlet CNT. The ability to detect a single fiber in a large tissue section affords a very high detection limit. For instance, a typical animal inhalation exposure at 5 mg/m3 contains 1.4 × 1010 particles . On average, a singlet MWCNT fiber of this aerosol would weigh 0.4 picograms. A typical section from a mouse is approximately 2 cm by 2 cm by 0.0005 cm deep or 0.002 cm3. Assuming the detection limit is one fiber per section, identification of a singlet MWCNT in a tissue section represents the ability to detect less than a nanogram of fibers per gram of tissue. Enhanced darkfield microscopy has been applied for detection and analysis of nanoparticles within the lungs from a variety of exposure [23–25]. In the present study, based on Table 1, the percentage of lung burden transported to the diaphragm at 1 day post-exposure was 0.00025 percent. This is equivalent to detection of 3 singlet MWCNT in the diaphragm for every million MWCNT fibers initially deposited in the lungs.
We have previously shown that exposure to MWCNT results in significant fiber accumulations within the interstitial spaces of the lungs, the lymphatics and the visceral pleura [2, 6, 27, 32]. The MWCNT structures within these sites were generally composed of single fibers or structures containing a few fibers, while MWCNT structures with a greater number of fibers remained in the airspaces and within alveolar macrophages of the lungs. The present study extends those results to demonstrate that MWCNT deposited in the lungs are transported to the pleura and/or extrapulmonary organs. The magnitude of extrapulmonary transport can be evaluated by expressing the lung burden transported in terms of fiber number translocated to the extrapulmonary organs (liver, kidney, hear and brain) relative to the initial number of fibers deposited in the lungs at 1 day post-exposure. Expressing the results of Table 1 in that manner, approximately 1 fiber deposits in an extrapulmonary organ for every 25,700 MWCNT fibers of lung burden present in the lungs at 1 day post-exposure after a 12 day exposure period. Transport during the post-exposure period from 1 day to 336 days significantly elevated the accumulation in extrapulmonary tissues with approximately 1 fiber for every 2,800 fibers present in the lungs at 1 day post-exposure being transported to extra-pulmonary tissues.
The significance of these levels of transport depends on the critical target for health risk assessment. At the cellular level, the mouse lung  and liver  contain approximately 119 billion and 15 billion cells, respectively. Dividing these cell numbers by the respective fiber counts (Table 1) demonstrates that, in the lungs, at 1 day post-exposure there is approximately 1 MWCNT fiber per 90 lung cells. In the liver at 1 day post-exposure, there is approximately 1 fiber per 381,650 liver cells and 1 fiber per 41,600 liver cells at 336 days post-exposure. These results clearly demonstrate that mass-action effects such as fibrosis are unlikely in extrapulmonary organs at these levels of transport. On the other hand, recent studies  have demonstrated that MWCNT fibers have highly efficient mutagenic effects which could prove to be a health risk concern for neoplastic development.
Donaldson et al.  raised concern that high aspect ratio CNT may, like asbestos, induce mesothelioma. Indeed, Takagi et al.  reported that intraperitoneal injection of MWCNT (3 ug/mouse) led to mesothelioma of the abdominal wall. Murphey et al.  reported persistent inflammation and fibrosis of the parietal pleural surface 24 weeks after intrapleural injection of long (>15 um) but not short (<4 um) MWCNT (5 ug/mouse). Therefore, there is great interest in determining whether pulmonary exposure to MWCNT leads to migration of MWCNT into the pleura, quantifying the magnitude of this migration, and determing if pleural lesions result. Ryman-Rasmussen et al.  reported MWCNT in subpleural lung tissue after inhalation exposure in mice. Porter et al.  were the first to demonstrate that such subpleural MWCNT can pierce the surface of the lungs and enter the intrapleural space after aspiration of these nanoparticles. Mercer et al.  conducted quantitative microscopic morphometry of lung tissue from the Porter et al. study and reported 12,000 penetrations of MWCNT into the intrapleural space 2 months after aspiration of MWCNT (80 ug/mouse). The current study extends these results in the following manner: 1) lungs were exposed to MWCNT by inhalation of mice over 12 days to yield a lung burden of 28 ug/lung, 2) morphometric analysis of chest wall and diaphramattic tissue was conducted at 1 and 336 days post-exposure, and 3) the number of MWCNT in the ches wall and diaphragm was quantified. Results indicate that at 336 days after inhalation exposure 12,457 fibers were found in the chest wall while 5,292 fibers were found in the diaphragm. Whether this fiber burden in pleural tissue results in inflammation, lesions and/or transformation of mesothelial cells is currently being investigated in an ongoing inhalation study at NIOSH.
Recently, Schinwald et al.  determined the threshold fiber length which would result in pleural inflammation 1 week after intrapleural injection of silver nanofibers of well defined lengths. Results showed a distinct length threshold, with fibers longer than 4 um leading to a pathogenic response. The MWCNT fibers aerosolized in the current study have a mean length of 4.3 um . Of interest, singlet MWCNT found in the chest wall, diaphragm, and systemic tissue appear to be in the 7–8 um range. Although these fibers should be too short to cause frustrated phagocytosis, they appear to be long enough to be retained in the pleura as demonstrated for MWCNT harvested by pleural lavage 336 days post-exposure (Figure 4). Therefore, if the pleural burden is sufficiently high a pathogenic response may be expected.
The route by which MWCNT are transported to the extra-pulmonary cannot be directly determined from the results of this study. Given the low levels found in the extrapulmonary organs a number of routes are possible. Phagocytosis of MWCNT by circulating monocytes/macrophages and neutrophils which transiently passage via the circulation, may provide a significant route. Observation of MWCNT loaded circulating cells in the capillary bed of extrapulmonary organs would be expected if phagocytosis or other adherence to MWCNT in the lungs resulted in transport to extrapulmonary organs. The nearly exclusive transport of singlet MWCNT to extrapulmonary organs (Figures 1 and 3) suggests that this route is not significant. Specific attempts were made to identify MWCNT in cells within the hepatic sinuosoids of the liver but none were detected. However, cases which demonstrated singlet MWCNT apparently at, or within, the endothelial boundary of capillaries were observed. An example is shown by the singlet MWCNT in the nearly tangential section through a capillary of the brain in the lower right panel of Figure 3.
MWCNT cleared from the lungs via the macrophage-mucociliary escalator may be reabsorbed by the gastrointestinal tract. In whole-body inhalation exposures, which was the exposure method in our study, intestinal absorption of MWCNT ingested during preening of fur may also be a significant pathway. Reports on the contribution by gut absorption to systemic delivery of nanoparticles have come to differing results. Kreyling et al.  found less than 1 percent of deposited nanoparticles transported to systemic organs and did not find evidence for gut absorption of 15 or 80 nm radio-labeled iridium particle when comparing extrapulmonary transport by whole body inhalation, gavage and intratracheal instillation. In a subsequent study by this group, using radiolabelled ultrafine carbon particles, Oberdörster et al.  found significant transport to the liver in whole body exposures of the rat and concluded that differences in translocation between the different nanoparticles may reflect differences in chemistry of the particles or gut absorption.
Finally the tracheobronchial lymphatic are a major route for fluid exchange of the lungs. Macrophage mediated transport through the lymphatic network has been shown to be important in particulate clearance from the lungs . The high lymphatic burdens observed 1 day post-exposure and at 336 days post-exposure (Table 1, Figures 2 and 4) indicate that the transport of MWCNT thru the lymphatics and ultimately into the venous circulation may be a major route for systemic delivery of MWCNT. Consistent with this role, dilation of peribronchiolar lymphatics was noted in the present study, as well as our previous acute inhalation exposures . However, direct measurements of MWCNT in the venous outflow from the lymphatics will be necessary to demonstrate the potential significance of this route.
One day after a 12 day inhalation exposure period MWCNT fibers were found throughout a wide range of lung associated tissues (lymph nodes, chest wall, diaphragm) and in extrapulmonary organs. Over the post-exposure period of 336 days, the lymph nodes accumulated a substantial fraction of 1 day post-exposure lung burden, while the levels in extrapulmonary organs increased approximately 6 to 7 fold. Inhaled MWCNT are capable of wide-spread dissemination and accumulation throughout the body. Outside the lungs and tracheobronchial lymph nodes the levels of accumulation are not likely to pose a risk of fibrosis. However, by 336 days post-exposure, the concentration of MWCNT per gram of tracheobronchial lymph nodes exceeds that in the lungs and is likely to produce adverse reactions, as those reported previously after exposure of mice by aspiration .
The slow rate at which MWCNT are cleared from the lungs by normal macrophage-mediated processes coupled with the high concentration in the tracheobronchial lymph nodes and the chronic accumulation in extrapulmonary organs and pleural associated tissue clearly demonstrate the need to address concerns about potential extra-pulmonary health effects from inhalation exposures to MWCNT.
Male C57BL/6 J mice (7 weeks old) were obtained from Jackson Laboratories (Bar Harbor, ME). Mice were housed one per cage in polycarbonate ventilated cages, which were provided HEPA-filtered air, with fluorescent lighting from 0700 to 1900 hours. Autoclaved Alpha-Dri virgin cellulose chips and hardwood Beta-chips were used as bedding. Mice were monitored to be free of endogenous viral pathogens, parasites, mycoplasms, Helicobacter and CAR Bacillus. Mice were maintained on Harlan Teklad Rodent Diet 7913 (Indianapolis, IN), and tap water was provided ad libitum. Animals were allowed to acclimate for at least 5 days before use. All animals used in this study were housed in an AAALAC-accredited; specific pathogen-free, environmentally controlled facility. All animal procedures were approved by the NIOSH ACUC.
Carbon nanotube source
MWCNT used in this study were obtained from Hodogaya Chemical Company (MWNT-7, lot #061220-31) and were manufactured using a floating reactant catalytic chemical vapor deposition method followed by high thermal treatment in argon at 2500°C furnace. This lot of MWCNT was fully characterized in our prior report in which acute inhalation exposures were conducted with this lot of MWCNT . Briefly, MWCNT trace metal contamination was 1.32%, with iron (1.06%) being the major metal contaminants. The bulk MWCNT were analyzed using several different techniques; 1) high resolution TEM, 2) XPS, and 3) electron spin resonance spectroscopy and are described in detail . Bulk and aerosol MWCNT morphology, were also analyzed by TEM and SEM in that study and found to have a similarity in particle shape and configuration to those collected from the breathing zones of a MWCNT manufacturing workplace .
MWCNT aerosol generation and aerosol characterization
Mice were exposed to a MWCNT aerosol (5 mg/m3, 5 hours/day) for 12 days, using an acoustical-based computer controlled system designed and constructed by our laboratory . Details of the exposure system, aerosol control performance and aerosol characterization have previously been published . In brief, the inhalation exposure system combines air flow controllers, aerosol particle monitors, data acquisition devices, and custom software with automated feedback control to achieve constant and repeatable exposure chamber temperature, relative humidity, pressure, aerosol concentration, and particle size distributions. The generator produces airborne particles continuously for long periods of time, e.g. 35 hours of continuous operation, with minimal fluctuations during an exposure period. The uniformity of test atmosphere in the chamber was evaluated to have a total variation of < 5%. In this study, the MWCNT aerosol mass concentration was continuously monitored with a Data RAM (DR-40000 Thermo Electron Co, Franklin, MA), and gravimetric determinations (37 mm cassettes with 0.45 μm pore-size Teflon filters) were used to calibrate and verify the Data RAM readings. The mass mode aerodynamic diameter was 1.3 μm with a count mode aerodynamic diameter of 0.42 μm . When characterized by lognormal statistics, the distribution was shown to have a mass median aerodynamic diameter (MMAD) of 1.5 μm and a geometric standard deviations (GSD) of 1.67 .
In the prior acute MWCNT inhalation study, run concurrently with this chronic study, the MWCNT lung burden in the mouse at 1 day post-exposure was determined to be 28.1 ug/lung . Workplace MWCNT-containing airborne dust levels of approximately 400 μg/m3 have been reported in a research laboratory  while a later study reported the highest total particle concentration of 320 μg/m3 with a mean of 106 μg/m3 based on results obtained from monitoring total workplace dust levels at seven MWCNT facilities . Assuming a level of one-tenth of the reported workplace range (10–40 ug/m3) Porter et al.  demonstrated that human worker exposure to MWCNT, performing light work for approximately 8.5 years in a work environment would be expected to produce a similar concentration of MWCNT in terms of micrograms per square meter of alveolar epithelial surface area in the human worker lungs as this inhalation study produced in the mouse lung. Thus the current mouse exposure represents an approximate feasible human occupational exposures.
Lavage of the pleural space was conducted prior to the instillation of fixative in an additional group of mice at 336 days post-exposure and in a corresponding clean-air group. Mice were deeply euthanized with an i.p. injection of sodium pentobarbital (>100 mg/kg body weight). For pleural lavage, a midline incision of the abdomen was made and a small cut made in the diaphragm. A blunted plastic tube connect to a 1 ml syringe was then used to slowly infuse and withdraw 1 ml of ice cold Ca2+ and Mg2+-free phosphate buffered saline, pH 7.4, supplemented with 5.5 mM D-glucose (PBS) into the pleural space 5 times. Slides were prepared from 0.2 ml aliquots using a cytocentrifuge (Shandon Elliot Cytocentrifuge, London). The cytospin preparations were stained with modified Wright-Giemsa stain and MWCNT fibers counted by scanning the entire sample at 60x magnification with an enhanced darkfield microscope.
Lung fixation and section preparation
At 1 day and 336 days after the 12 day exposure period, mice were euthanized by an overdose of pentobarbital (>100 mg/kg body weight, i.p.) and lungs and extrapulmonary tissues were preserved by whole body vascular perfusion of paraformaldehyde while the lungs were inflated with air. Separate, clean-air control groups were studied.
For whole body perfusion the trachea was cannulated, the lungs inflated with 1 ml of air and a midline incision of the chest was made to expose the heart and lungs. The left ventricle of the heart was punctured with a large bore needle connected to a reservoir 100 cm above the chest wall of the animal. In quick sucession the right atrium was cut, to allow outflow, the reservoir valve was opened to allow perfusion of the whole body with clearing solution (heparinized saline). After the clearing solution was passed (2 to 5 ml), the reservoir was switched to paraformaldehyde and the whole body perfusion fixed (~ 25 to 50 ml).
Following fixation the tracheobronchial lymph nodes, diaphragm, heart, kidney, liver and brain were removed, and sliced into 5–6 mm thick tissue blocks and embedded in paraffin. The left lung was removed, cut into a coronal mid-section and processed independently to avoid potential for contamination. The chest wall was decalcified in formic acid prior to embedding. Sections (5 micron thick) were collected on ultrasonically cleaned, laser cut slides (Schott North America, Inc, Elmsford, N.Y. 10523) to avoid nanoparticle contamination from the ground edges of traditional slides. To enhance the contrast between tissue and MWCNT, sections were stained with Sirius Red. Sirius Red staining consisted of immersion of the slides in 0.1% Picrosirius solution (100 mg of Sirius Red F3BA in 100 ml of saturated aqueous picric acid, pH 2) for 1 hour followed by washing for 1 minute in 0.01 N HCl. Sections were then briefly counterstained in freshly filtered Mayer’s hematoxylin for 2 minutes, dehydrated, and coverslipped. For serial section analysis to determine the mean caliper diameter of MWCNTs in tissue, five serial sections of the lungs (3 um thick) were collected on one slide and stained as described above.
Field emission scanning electron microscopy
For scanning electron microscopy, sections of the lung were cut at 8 microns, placed on carbon planchets, deparaffinized and sputter coated. After coating, the specimens were examined with a Hitachi Model S-4800 Field Emission Scanning Electron Microscope (FESEM) at 5 to 10 kV and at working distances of 4.5 mm to 6 mm for magnifications of 100,000× to 1000×, respectively. Photographs were taken in slow scanning mode at 1280 × 1024 pixels. Use of thin sections from paraffin embedded tissue was found to be preferable to large, unevenly cut blocks because it provided a uniform thickness of organic material on the carbon planchet. The 8 micron sections were thick enough to convey three-dimensional information but were also less likely to charge or undergo physical shifts when examined at the high magnifications necessary to study nanomaterials.
Enhanced-darkfield light microscopy imaging of nanoparticles
Carbon nanotubes in sections from exposed lungs were assessed using an enhanced-darkfield optical system. Using this method of imaging, lung sections can be easily scanned at relatively low magnification to identify CNTs that would not be detected by other means. Nanomaterials, such as carbon nanotubes, have dimensions less than the wavelength of light, have closely packed atoms, and typically have a refractive index significantly different from that of biologic tissues and/or mounting medium. These characteristics produce significantly greater scattering of light by nanoparticles than by the surrounding tissues. The enhanced-darkfield optical system images light scattered in the section and, thus, nanomaterials in the section stand-out from the surrounding tissues with high contrast. Detection of a nanomaterial in a section thus depends on the ability of the particle to scatter light and the number of scattered photons required for detection by the imaging system.
In practice enhanced darkfield has been found to be an essential tool to detect and measure MWCNT regional pulmonary distribution  and in detection of MWCNT systemic transport following inhalation in the rat . Detection and quantitiatve assessment of other nanoparticles has been reported. These include the diesel fuel catalyst, cerium oxide , titanium dioxide nanospheres , titanium dioxide nanospheres and nanobelts  and summarized in a review article on pathologic assessment of nanoparticles which describes aspects of enhanced darkfield in nanoparticle detection .
The optical system for enhanced darkfield microscopy consisted of high signal-to-noise, darkfield-based illumination optics adapted to an Olympus BX-41 microscope (CytoViva, Auburn, AL 36830). Sections for dark-field examination were specifically cut from paraffin blocks and collected on ultrasonically cleaned, laser cut slides (Schott North America Inc, Elmsford, N.Y. 10523) to avoid nanoparticle contamination from the ground edges of traditional slides. After staining with Sirius Red-Hematoxylin, sections were coverslipped with Permount. After alignment of the substage oil immersion optics with a 10x objective, sections were examined with 60x or 100x oil immersion objectives. Enhanced darkfield images were taken with a 2048 × 2048 pixel digital camera (Dage-MTI Excel digital camera XLMCT, Michigan City, In 46360).
Number of MWCNT fibers in diaphragm, chest wall and extrapulmonary organs
Formula for number of singlet MWCNT in organ
Number per unit area cm2
Mean caliper diameter of singlet MWCNT cm
Section thickness cm
Organ Volume = Organ Weight gm × 1 cm3/gm
Number per unit volume #/ cm3
Number per organ
Sections of clean-air control lungs were scanned as well for fibers but were negative for the presence of MWCNT fibers. Total MWCNT fiber number of 1,321 million was used for the lung based on previously reported measurements of 1 day post-exposure lung burden of MWCNT fibers of 28.1 ug/lung previously determined for this inhalation study  and a conversion of 47 million MWCNT fibers per ug .
Measurement of singlet MWCNT fiber length in lungs, liver and kidney
Optical sectioning through a series of serial sections in lung, liver and kidney was used to measure the length of singlet MWCNT at 1 and 336 days after the termination of inhalation exposure. Serial sections consisted of 4–5 sections, 5 um thick, mounted on a single slide. For each tissue/series (lungs or systemic organs) the second section of each series was scanned for singlet MWCNT using enhanced darkfield illumination with a high numerical aperture, 100x oil immersion objective. When a singlet MWCNT was identified in the second section, it was selected for measurement if it did not continue down into the first section to produce an unbiased (length independent) sampling. Thus singlet MWCNT were selected for measurement if they began in the second section. In the second section of each selected singlet, the lower-most end was focused on, photographed and the depth (Z co-ordinate on focus knob) recorded. A point mid-fiber in the section (or at a sharp bend/inflection point if present) was next focused, photographed and the depth (Z co-ordinate) recorded. Finally, the upper-most end of the singlet was focused on, photographed and the depth (z co-ordinate) recorded. If the singlet continued in the adjacent upper section(s) the process of focus, photography and Z-co-ordinate measurement was repeated to the end of the singlet. ImageJ was then used to measure the X-Y co-ordinates of the singlet/middle points. The length of the singlet was then calculated from the 3-dimensional distance from one end through the middle to the other end (including adjacent sections if the singlet was not completely contained within a section). Approximately 20 singlet MWCNT were measured in each lung, liver and kidney in 5 animals at 1 and 336 days after the inhalation exposure.
Measurement of MWCNT content in tracheobronchial lymph nodes
Direct counting of MWCNT in tracheobronchial lymph nodes was not possible due to the dense aggregations beyond 1 day post-exposure. Instead, the volume density of MWCNT relative to the volume density of MWCNT in the lung at 1 day post-exposure was used to determine the lymph node content. For this purpose, 6–12 photographs were taken at 60x uniformly distributed across the mid-section profile of the capsule of each lymph node and across the mid-section of the left lung. Each section was thresholded to produce white for MWCNT and black for air/tissue and the volume proportion determined using ImageJ. The accuracy of this procedure was verified by direct comparison of a sample of photograph to manual point counting which produced volume densities for MWCNT that were within 1% of the threshold image determined values. The mass of MWCNT in the tracheobronchial lymph nodes was then obtained by multiplying the lung burden times the ratio of volume densities, which was then multiplied by the ratio of tracheobronchial lymph node volume to lung volume.
Direct weighing of the tracheobronchial lymph nodes was not suitable to determine the capsule volume of the nodes where MWCNT were found. Unlike extrapulmonary organs, dissected tracheobronchial lymph nodes have a high mass of associated adventitia which cannot be removed without risk of damage to the nodes where the MWCNT are concentrated. To avoid injury to the capsule, which was also needed for pathological assessment, the entire dissected tracheobronchial lymph node was embedded and a mid-block tissue section photographed. The area of the capsule of the tracheobronchial lymph nodes was then used to calculate the organ weight assuming a tissue density of 1 gm/cm3.
Data were analyzed using analysis of variance (STATGRAF). Bartlett’s test was used to test for homogeneity of variances between groups. Statistical differences were determined using one-way analysis of variance with significance set at p ≤ 0.05. When significant F values were obtained, individual means at 336 days post-exposure were compared to corresponding 1 day post-exposure for the corresponding organ using Duncan’s multiple range test , and P < 0.05 was considered to be significant. Data are given as Means ± S.E.
Field emission scanning electron microscope
Geometric standard deviations
Mass median aerodynamic diameter
Multi-walled carbon nanotubes
Transmission electron microscope.
We appreciate Dean Newcomer and Patsy Willard for their excellent technical assistance with the histologic preparation and staining of the slides. Diane Schwegler-Berry assisted with the preparation of FESEM samples. The authors would like to thank Hodogaya Chemical Company, for the generous donation of the MWCNT used in this study.
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.
- Dahm MM, Evans DE, Schubauer-Berigan MK, Birch ME, Deddens JA: Occupational exposure assessment in carbon nanotube and nanofiber primary and secondary manufacturers mobile direct-reading sampling. Ann Occup Hyg 2013,57(3):328–44. 10.1093/annhyg/mes079PubMed CentralView ArticlePubMedGoogle Scholar
- Porter DW, Hubbs AF, Mercer RR, Wu N, Wolfarth MG, Sriram K, Leonard S, Battelli LA, 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.2009.10.017View ArticlePubMedGoogle Scholar
- Li JG, Li WX, Xu JY, Cai XQ, Liu RL, Li YJ, Zhao QF, Li QN: Comparative study of pathological lesions induced by multiwalled carbon nanotubes in lungs of mice by intratracheal instillation and inhalation. Environ Toxicol 2007, 22: 415–421. 10.1002/tox.20270View ArticlePubMedGoogle Scholar
- Ryman-Rasmussen JP, Tewksbury EW, Moss OR, Cesta MF, Wong BA, Bonner JC: Inhaled multiwalled carbon nanotubes potentiate airway fibrosis in murine allergic asthma. Am J Respir Cell Mol Biol 2009, 40: 349–358. 10.1165/rcmb.2008-0276OCPubMed CentralView ArticlePubMedGoogle Scholar
- Pauluhn J: Subchronic 13-week inhalation exposure of rats to multiwalled carbon nanotubes: toxic effects are determined by density of agglomerate structures, not fibrillar structures. Toxicol Sci 2010, 113: 226–242. 10.1093/toxsci/kfp247View ArticlePubMedGoogle Scholar
- Mercer RR, Hubbs AF, Scabilloni JF, Wang LY, Battelli LA, Schwegler-Berry D, Castranova V, Porter DW: Distribution and persistence of pleural penetrations by multi-walled carbon nanotubes. Partitcle Fibre Toxicol 2010, 7: 28. 10.1186/1743-8977-7-28View ArticleGoogle Scholar
- Xu J, Futakuchi M, Shimizu H, Alexander DB, Yanagihara K, Fukamachi K, Suzui M, Kanno J, Hirose A, Ogata A, et al.: Multi-walled carbon nanotubes translocate into the pleural cavity and induce visceral mesothelial proliferation in rats. Cancer Sci 2012, 103: 2045–2050. 10.1111/cas.12005View ArticlePubMedGoogle Scholar
- Ryman-Rasmussen JP, Cesta MF, Brody AR, Shipley-Phillips JK, Everitt JI, Tewksbury EW, Moss OR, Wong BA, Dodd DE, Andersen ME, Bonner JC: Inhaled carbon nanotubes reach the subpleural tissue in mice. Nat Nanotechnol 2009, 4: 747–751. 10.1038/nnano.2009.305PubMed CentralView ArticlePubMedGoogle Scholar
- Sriram K, Porter DW, Jefferson AM, Lin GX, Wolfarth MG, Chen BT, McKinney W, Frazer DG, Castranova V: Neuro inflammation and blood–brain barrier changes following exposure to engineered nanomaterials. The Toxicologist 2009, 108: A2197.Google Scholar
- Li Z, Salmen R, Huldermen T, Kisin ER, Shvedova AA, Luster M, Simeonova P: Pulmonary exposure to carbon nanotubes induces vascular toxicity. The Toxicologist 2005, 84: A1045.Google Scholar
- Erdely A, Hulderman T, Salmen R, Liston A, Zeidler-Erdely PC, Schwegler-Berry D, Castranova V, Koyama S, Kim YA, Endo M, Simeonova PP: Cross-talk between lung and systemic circulation during carbon nanotube respiratory exposure. Nano Lett 2009, 9: 36–43. 10.1021/nl801828zView ArticlePubMedGoogle Scholar
- Stapleton PA, Minarchick V, Cumpston A, McKinney W, Chen BT, Frazer D, Castranova V, Nurkiewicz TR: Time-course of improved coronary arteriolar endothelium-dependent dilation after multi-walled carbon nanotube inhalation. The Toxicologist 2011, 120: A2197.Google Scholar
- Sargent LM, Hubbs AF, Young SH, Kashon ML, Dinu CZ, Salisbury JL, Benkovic SA, Lowry DT, Murray AR, Kisin ER, et al.: Single-walled carbon nanotube-induced mitotic disruption. Mutat Res 2012, 745: 28–37. 10.1016/j.mrgentox.2011.11.017View ArticlePubMedGoogle Scholar
- Pacurari M, Qian Y, Porter DW, Wolfarth M, Wan Y, Luo D, Ding M, Castranova V, Guo NL: Multi-walled carbon nanotube-induced gene expression in the mouse lung: association with lung pathology. Toxicol Appl Pharmacol 2011, 255: 18–31. 10.1016/j.taap.2011.05.012PubMed CentralView ArticlePubMedGoogle Scholar
- Singh R, Pantarotto D, Lacerda L, Pastorin G, Klumpp C, Prato M, Bianco A, Kostarelos K: Tissue biodistribution and blood clearance rates of intravenously administered carbon nanotube radiotracers. PNAS 2006, 103: 3357–3362. 10.1073/pnas.0509009103PubMed CentralView ArticlePubMedGoogle Scholar
- Kreyling W, Semmler M, Erbe F, Mayer P, Takenaka S, Schulz H: Translocation of ultrafine insoluble iridium particles from lung epithelium to extrapulmonary organs is size dependent but very low. J Toxicol Environ Health A 2002, 65: 1513–1530. 10.1080/00984100290071649View ArticlePubMedGoogle Scholar
- Oberdörster G, Sharp Z, Atudorei V, Elder A, Gelein R, Lunts A, Kreyling W, Cox C: Extrapulmonary translocation of ultrafine carbon particles following whole-body inhalation exposure of rats. J Toxicol Environ Health A 2002, 65: 1531–1543. 10.1080/00984100290071658View ArticlePubMedGoogle Scholar
- Cho C, Cho WS, Choi M, Kim SJ, Han BS, Kim SH, Kim HO, Sheen YY, Jeong J: The impact of size on tissue distribution and elimination by single intravenous injection of silica nanoparticles. Toxicol Lett 2009, 189: 177–183. 10.1016/j.toxlet.2009.04.017View ArticlePubMedGoogle Scholar
- Kwon JT, Hwang SK, Jin H, Kim DS, Minai-Tehrani A, Yoon HJ, Choi M, Yoon TJ, Han DY, Kang YW, et al.: Body distribution of inhaled fluorescent magnetic nanoparticles in the mice. J Occup Health 2008, 50: 1–6. 10.1539/joh.50.1View ArticlePubMedGoogle Scholar
- Sonavane G, Tomoda K, Makino K: Biodistribution of colloidal gold nanoparticles after intravenous administration: effect of particle size. Colloids Surf B Biointerfaces 2008, 66: 274–280. 10.1016/j.colsurfb.2008.07.004View ArticlePubMedGoogle Scholar
- Mantel M: Limits of detection of trace elements in biological materials analysed by instrumental neutron activation analysis using X-ray spectrometry and magnetic deflection of beta-rays. Analyst 1983, 108: 1190–1194. 10.1039/an9830801190View ArticlePubMedGoogle Scholar
- Scott MC, Chettle DR: In vivo elemental analysis in occupational medicine. Scand J Work Environ Health 1986, 12: 81–96. 10.5271/sjweh.2162View ArticlePubMedGoogle Scholar
- Ma JY, Mercer RR, Barger M, Schwegler-Berry D, Scabilloni J, Ma JK, Castranova V: Induction of pulmonary fibrosis by cerium oxide nanoparticles. Toxicol Appl Pharmacol 2012, 262: 255–264. 10.1016/j.taap.2012.05.005View ArticlePubMedGoogle Scholar
- McKinney W, Jackson M, Sager TM, Reynolds JS, Chen BT, Afshari A, Krajnak K, Waugh S, Johnson C, Mercer RR, et al.: Pulmonary and cardiovascular responses of rats to inhalation of a commercial antimicrobial spray containing titanium dioxide nanoparticles. Inhal Toxicol 2012, 24: 447–457. 10.3109/08958378.2012.685111View ArticlePubMedGoogle Scholar
- Porter DW, Wu N, Hubbs AF, Mercer RR, Funk K, Meng F, Li J, Wolfarth MG, Battelli L, Friend S, et al.: Differential mouse pulmonary dose and time course responses to titanium dioxide nanospheres and nanobelts. Toxicol Sci 2013, 131: 179–193. 10.1093/toxsci/kfs261PubMed CentralView ArticlePubMedGoogle Scholar
- Stapleton PA, Minarchick VC, Cumpston AM, McKinney W, Chen BT, Sager TM, Frazer DG, Mercer RR, Scabilloni J, Andrew ME, et al.: Impairment of coronary arteriolar endothelium-dependent dilation after multi-walled carbon nanotube inhalation: a time-course study. Int J Mol Sci 2012, 13: 13781–13803. 10.3390/ijms131113781PubMed CentralView ArticlePubMedGoogle Scholar
- Porter DW, Hubbs AF, Chen BT, McKinney W, Mercer RR, Wolfarth MG, Battelli L, Wu N, Sriram K, Leonard S, et al.: Acute pulmonary dose-responses to inhaled multi-walled carbon nanotubes. Nanotoxicology 2012. Epud ahead of printGoogle Scholar
- Aiso S, Kubota H, Umeda Y, Kasai T, Takaya M, Yamazaki K, Nagano K, Sakai T, Koda S, Fukushima S: Translocation of intratracheally instilled multiwall carbon nanotubes to lung-associated lymph nodes in rats. Ind Health 2011, 49: 215–220. 10.2486/indhealth.MS1213View ArticlePubMedGoogle Scholar
- Choe N, Tanaka S, Xia W, Hemenway DR, Roggli VL, Kagan E: Pleural macrophage recruitment and activation in asbestos-induced pleural injury. Environ Health Perspect 1997,105(Suppl 5):1257–1260. 10.1289/ehp.97105s51257PubMed CentralView ArticlePubMedGoogle Scholar
- Stott WT, Dryzga MD, Ramsey JC: Blood-flow distribution in the mouse. J Appl Toxicol 1983, 3: 310–312. 10.1002/jat.2550030607View ArticlePubMedGoogle Scholar
- Chen BT, Schwegler-Berry D, McKinney W, Stone S, Cumpston JL, Friend S, Porter DW, Castranova V, Frazer DG: Multi-walled carbon nanotubes: sampling criteria and aerosol characterization. Inhal Toxicol 2012, 24: 798–820. 10.3109/08958378.2012.720741View ArticlePubMedGoogle Scholar
- Mercer RR, Hubbs AF, Scabilloni JF, Wang L, Battelli LA, Friend S, Castranova V, Porter DW: Pulmonary fibrotic response to aspiration of multi-walled carbon nanotubes. Part Fibre Toxicol 2011, 8: 21. 10.1186/1743-8977-8-21PubMed CentralView ArticlePubMedGoogle Scholar
- Stone KC, Mercer RR, Gehr P, Stockstill B, Crapo JD: Allometric relationships of cell numbers and size in the mammalian lung. Am J Respir Cell Mol Biol 1992, 6: 235–243. 10.1165/ajrcmb/6.2.235View ArticlePubMedGoogle Scholar
- Atchley WR, Wei R, Crenshaw P: Cellular consequences in the brain and liver of age-specific selection for rate of development in mice. Genetics 2000, 155: 1347–1357.PubMed CentralPubMedGoogle 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 CentralView ArticlePubMedGoogle Scholar
- Takagi A, Hirose A, Nishimura T, Fukumori N, Ogata A, Ohashi N, Kitajima S, Kanno J: Induction of mesothelioma in p53+/− mouse by intraperitoneal application of multi-wall carbon nanotube. J Toxicol Sci 2008, 33: 105–116. 10.2131/jts.33.105View ArticlePubMedGoogle Scholar
- Murphy FA, Poland CA, Duffin R, Al-Jamal KT, Ali-Boucetta H, Nunes A, Byrne F, Prina-Mello A, Volkov Y, Li S, et al.: Length-dependent retention of carbon nanotubes in the pleural space of mice initiates sustained inflammation and progressive fibrosis on the parietal pleura. Am J Pathol 2011, 178: 2587–2600. 10.1016/j.ajpath.2011.02.040PubMed CentralView ArticlePubMedGoogle Scholar
- Schinwald A, Murphy FA, Prina-Mello A, Poland CA, Byrne F, Movia D, Glass JR, Dickerson JC, Schultz DA, Jeffree CE, et al.: The threshold length for fiber-induced acute pleural inflammation: shedding light on the early events in asbestos-induced mesothelioma. Toxicol Sci 2012, 128: 461–470. 10.1093/toxsci/kfs171View ArticlePubMedGoogle Scholar
- Harmsen AG, Muggenburg BA, Snipes MB, Bice DE: The role of macrophages in particle translocation from lungs to lymph nodes. Science 1985, 230: 1277–1280. 10.1126/science.4071052View ArticlePubMedGoogle Scholar
- Han JH, Lee EJ JHL, So KP, Lee YH, Bae GN, Lee S-B, Cho MH, Yu IE: Monitoring multiwalled carbon nanotube exposure in carbon nanotube research facility. Inhal Toxicol 2008, 20: 741–749. 10.1080/08958370801942238View ArticlePubMedGoogle Scholar
- McKinney W, Chen B, Frazer D: Computer controlled multi-walled carbon nanotube inhalation exposure system. Inhal Toxicol 2009, 21: 1053–1061. 10.1080/08958370802712713View ArticlePubMedGoogle Scholar
- Lee JH, Lee S-B, Bae GN, Jeon KS, Yoon JU, Ji JH, Sung JH, Lee BG, Lee JH, Yang JS, et al.: Exposure assessment of carbon nanotube manufacturing workplaces. Inhal Toxicol 2010, 22: 369–381. 10.3109/08958370903367359View ArticlePubMedGoogle Scholar
- Hubbs AF, Sargent LM, Porter DW, Sager TM, Chen BT, Frazer DG, Castranova V, Sriram K, Nurkiewicz TR, Reynolds SH, et al.: Nanotechnology: toxicologic pathology. Toxicol Pathol 2013, 41: 395–409. 10.1177/0192623312467403View ArticlePubMedGoogle Scholar
- Scabilloni JF, Wang L, Antonini JM, Roberts JR, Castranova V, Mercer RR: Matrix metalloproteinase induction in fibrosis and fibrotic formation due to silica inhalation. Am J Physiol Lung Cell Mol Physiol 2005, 288.Google Scholar
- Mercer RR, Crapo JD: Three-dimensional reconstruction of the rat acinus. J Appl Physiol 1987, 63: 785–794.PubMedGoogle Scholar
- Mercer RR, Russell ML, Roggli VL, Crapo JD: Cell number and distribution in human and rat airways. Am J Respir Cell Mol Biol 1994, 10: 613–624. 10.1165/ajrcmb.10.6.8003339View ArticlePubMedGoogle Scholar
- Hillard JE: The counting and sizing of particles in transmission microscopy. Met Soc AIME-Trans 1962, 224: 906–917.Google Scholar
- Duncan DB: Multiple range and multiple F tests. Biometrics 1955, 11: 1–42. 10.2307/3001478View ArticleGoogle Scholar
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