Promotion of lung adenocarcinoma following inhalation exposure to multi-walled carbon nanotubes
- Linda M Sargent1Email author,
- Dale W Porter1,
- Lauren M Staska2,
- Ann F Hubbs1,
- David T Lowry1,
- Lori Battelli1,
- Katelyn J Siegrist1,
- Michael L Kashon1,
- Robert R Mercer1,
- Alison K Bauer3,
- Bean T Chen1,
- Jeffrey L Salisbury4,
- David Frazer1,
- Walter McKinney1,
- Michael Andrew1,
- Shuji Tsuruoka5,
- Morinobu Endo5,
- Kara L Fluharty1,
- Vince Castranova1 and
- Steven H Reynolds1
© Sargent et al.; licensee BioMed Central Ltd. 2014
Received: 14 June 2013
Accepted: 6 November 2013
Published: 9 January 2014
Engineered carbon nanotubes are currently used in many consumer and industrial products such as paints, sunscreens, cosmetics, toiletries, electronic processes and industrial lubricants. Carbon nanotubes are among the more widely used nanoparticles and come in two major commercial forms, single-walled carbon nanotubes (SWCNT) and the more rigid, multi-walled carbon nanotubes (MWCNT). The low density and small size of these particles makes respiratory exposures likely. Many of the potential health hazards have not been investigated, including their potential for carcinogenicity. We, therefore, utilized a two stage initiation/promotion protocol to determine whether inhaled MWCNT act as a complete carcinogen and/or promote the growth of cells with existing DNA damage. Six week old, male, B6C3F1 mice received a single intraperitoneal (ip) injection of either the initiator methylcholanthrene(MCA, 10 μg/g BW, i.p.), or vehicle (corn oil). One week after i.p. injections, mice were exposed by inhalation to MWCNT (5 mg/m3, 5 hours/day, 5 days/week) or filtered air (controls) for a total of 15 days. At 17 months post-exposure, mice were euthanized and examined for lung tumor formation.
Twenty-three percent of the filtered air controls, 26.5% of the MWCNT-exposed, and 51.9% of the MCA-exposed mice, had lung bronchiolo-alveolar adenomas and lung adenocarcinomas. The average number of tumors per mouse was 0.25, 0.81 and 0.38 respectively. By contrast, 90.5% of the mice which received MCA followed by MWCNT had bronchiolo-alveolar adenomas and adenocarcinomas with an average of 2.9 tumors per mouse 17months after exposure. Indeed, 62% of the mice exposed to MCA followed by MWCNT had bronchiolo-alveolar adenocarcinomas compared to 13% of the mice that received filtered air, 22% of the MCA-exposed, or 14% of the MWCNT-exposed. Mice with early morbidity resulting in euthanasia had the highest rate of metastatic disease. Three mice exposed to both MCA and MWCNT that were euthanized early had lung adenocarcinoma with evidence of metastasis (5.5%). Five mice (9%) exposed to MCA and MWCNT and 1 (1.6%) exposed to MCA developed serosal tumors morphologically consistent with sarcomatous mesotheliomas, whereas mice administered MWCNT or air alone did not develop similar neoplasms.
These data demonstrate that some MWCNT exposures promote the growth and neoplastic progression of initiated lung cells in B6C3F1 mice. In this study, the mouse MWCNT lung burden of 31.2 μg/mouse approximates feasible human occupational exposures. Therefore, the results of this study indicate that caution should be used to limit human exposures to MWCNT.
The nanotechnology industry is a multibillion dollar industry and is expected to reach a trillion dollars by 2015 . Carbon nanotubes are long thin nanoparticles that are composed of a single wall (SWCNT) or multiple walls (MWCNT) of graphene sheets rolled into tubes. MWCNT have potential applications in many consumer and industrial settings including medical devices, batteries, the automobile industry, electronic processes and the aerospace industry [2, 3]. Carbon nanotubes are light and easily aerosolized making workplace exposure to nanoparticles a potentially significant source of human exposure. The material resists degradation and may persist in the body for extended periods of time [4, 5]. The respiratory tract is a likely route of exposure due to the low density and small size of airborne nanoparticles. Similar to inhaled asbestos fibers, MWCNT deposited in the lungs of mice by pharyngeal aspiration or inhalation produced histologic changes including inflammation and fibrosis as well as hypertrophied and hyperplastic bronchiolar and alveolar epithelial cells [4, 6–8]. Additional changes in some alveolar epithelial Type II cells of MWCNT-exposed mice include cellular atypia . MWCNT can reach the alveolar region, the interstitium and the pleural space after both aspiration and inhalation [8–10]. Some macrophages that contain MWCNT particles have been observed without nuclei and with MWCNT connecting dividing chromosomes indicating that carbon nanotubes may be capable of inducing errors in cell division in vivo following either aspiration or inhalation exposure . Type II cells from rodents exposed to MWCNT been shown to have micronuclei, indicating either a higher level of chromosome damage or mitotic spindle disruption . In vitro investigations have demonstrated that carbon nanotubes disrupt the cell division apparatus and induce errors in chromosome number [11–14].
The multistage nature of cancer has been described in liver, skin and mammary as well as lung models for cancer [15–18]. Carcinogenic agents can act in one or all of the stages of the neoplastic process. Initiating agents typically cause a heritable change in DNA while tumor promoters induce proliferation of DNA damaged cells to form visible preneoplastic or benign clones . During the last stage of neoplastic development (progression) malignant characteristics, karyotypic instability and frank neoplasms appear . A complete carcinogen can act at all three stages. Cellular proliferation is a feature of the second phase of pulmonary carcinogenesis (promotion) [16, 17]. Of interest, epithelial hyperplasia and cellular atypia were observed in mice exposed to MWCNT in vivo . Therefore, the potential for carcinogenicity is of particular concern. In addition, previous studies have indicated the potential for carbon nanotubes to act during the progression of cells from preneoplastic and early benign lesions to carcinoma as shown by their ability to disrupt the mitotic spindle and induce chromosome alterations [17, 19]. Investigations of MWCNT carcinogenicity have demonstrated that intraperitoneal or intrascrotal injection of MWCNT results in mesotheliomas in p53 +/- transgenic mice and Fischer rats, respectively [20, 21]. The high-dose and agglomeration of the 3 mg MWCNT exposure used in the Takagi et al. study have been questioned, since it resulted in a high death rate due to gastrointestinal occlusion . However, a more recent study demonstrated the induction of mesothelioma after intraperitoneal injection of as little as 3 μg of MWCNT in mice . Because the physical properties of MWCNT make respiratory exposure likely during the production and processing of commercial products and pulmonary exposures in rodents have indicated a potential for genotoxicity, inflammation, cell proliferation, cellular atypia, and migration to the pleural space in a manner similar to other long thin fiber-like materials that are carcinogenic, there is an urgent need to examine the potential for cancer in an animal model following inhalation of carbon nanotubes.
The overall objective of this study was to determine whether inhalation of MWCNT produced lung tumors in adult, male B6C3F1 mice using a two-stage, initiation-promotion protocol. The B6C3F1 mouse is the strain used by the National Toxicology Program to evaluate chemicals for potential carcinogenicity . The B6C3F1 hybrid is of intermediate susceptibility for spontaneous lung tumor formation; however, the strain is less sensitive than the sensitive/intermediate 020 and BALB/cByJ strains [25, 26]. In addition, there is a wealth of information on the spontaneous tumor response and lifespan of the B6C3F1 mouse strain [25, 27–29]. This is the first investigation to examine the potential carcinogenicity of carbon nanotubes using a multi-stage carcinogenesis model in the B6C3F1 mouse lung.
Foreign material observed during histopathology assessment
Incidence of focal adenomatous hyperplasia, macrophage infiltration and foreign material in the lung by light microscopy
Focal alveolar adenomatous hyperplasia, macrophage infiltration and foreign material observed in MWCNT–treated mice 17 months following exposure
MCA + MWCNT
Number of animals/group
Number animals with positive foreign material
Number animals with positive for focal adenomatous alveolar hyperpasia
Enhanced darkfield imaging of MWCNT
Hyperplasia and macrophage infiltration in the lung
Incidences of macrophage infiltration were higher in the MWCNT or MCA + MWCNT groups relative to the air or MCA groups (Table 1). It was seen as occasional, random, small clusters of macrophages in airways or alveoli, or as slightly increased numbers in interstitial connective tissues often near terminal bronchioles or alveolar ducts.
Lung adenoma and adenocarcinoma
Incidence and multiplicity of lung tumors in B6C3F1 mice 17 months following exposure to Mitsui-7 MWCNT
Total number of mice
Percent of animals with tumors
Total number of lung tumors
Lung tumors/total number of animals
Number of adenocarcinomas/group
MCA + MWCNT
Incidence of lung tumors in early euthanized mice and mice 17 months after exposure
MCA + MWCNT
MCA + MWCNT
Number of animals
Number of Bronchiolo-alveolar adenomas
% of mice with one or more Bronchiolo-alveolar adenoma
Number of Bronchiolo-alveolar adenocarcinomas
% of mice with Bronchiolo-alveolar Adenocarcinomas
Number of mice with one or more– Bronchiolo-alveolar adenoma and/or Bronchio-alveolar adenocarcinomas
Percent of mice with lung tumors
Malignant serosal tumors in MCA + MWCNT Exposed Mice
MCA + MWCNT
Mesothelioma by animal #
Bronchial lymph node
Skeletal muscle diaphragm
The primary objective of this investigation was to evaluate if exposure to aerosolized MWCNT promotes the growth of DNA damaged cells and/or is a complete carcinogen. To accomplish this, mice were exposed to aerosolized MWCNT (5 mg/m3, 5 hours/day) for 15 days. Initial MWCNT lung burden in these mice was 31.2 ± 0.9 μg MWCNT/mouse . In order to evaluate the relationship of these MWCNT lung burdens to human MWCNT exposures, we compared the MWCNT lung burdens in these mice with potential human occupational exposures. OSHA has not yet established exposure limits for carbon nanotubes; however, MWCNT are regulated as respirable particulates not otherwise regulated (PNOR). The PNOR have an OSHA Permissible Exposure Limit (PEL) of 5 mg/m3. NIOSH recently published a Current Intelligence Bulletin with a Recommended Exposure Limit (REL) of 1 μg/m3 for carbon nanotubes which is 5000-fold lower than the OSHA PNOR PEL .
Assuming a mouse alveolar epithelium surface area of 0.05 m2, the 31.2 μg MWCNT lung burden would result in 624 μg MWCNT/m2 alveolar epithelium. Using the alveolar epithelial surface area of 102 m2 for human, the equivalent human lung burden would be 63.6 mg .
If the MWCNT mass median aerodynamic diameter (MMAD) =1.5 μm were used, minute ventilation of 20 L/minute for a person performing light work  and an alveolar deposition fraction of 30%  (for 240 work days per year), the equivalent lung burden in workers exposed at the previous draft REL for CNT of 7 μg/m3 would be achieved in approximately 13 years . This indicates that the mouse MWCNT lung burdens in this study approximate feasible human occupational exposures.
Inhalation of multi-walled carbon nanotubes (MWCNT) for 15 days following a single intraperitoneal injection of the known initiator MCA led to increased incidence and numbers of bronchiolo-alveolar adenomas and bronchiolo-alveolar adenocarcinomas in B6C3F1 male mice. The combined incidence of bronchiolo-alveolar adenomas and bronchiolo-alveolar carcinomas of 90.5% for the MCA + MWCNT group greatly exceeded that in groups of mice exposed to air or MCA and the NTP historical vehicle control range for B6C3F1 male mice . Additionally, the numbers of bronchiolo-alveolar adenomas or bronchiolo-alveolar adenocarcinomas were greatest in the MCA + MWCNT group compared to other groups. The data demonstrate that MWCNT may act as a carcinogen that promotes the growth of initiated lung cells, resulting in the development of lung adenocarcinoma.
The strong tumor promotion that was observed in the current study may have resulted from a combination of effects that have been observed following exposure to carbon nanotubes. MWCNT material was observed in the diaphragm and in the lungs, both within macrophages and the interstitium. MWCNT are internalized by macrophages following pulmonary exposure. In addition, MWCNT material has been observed in the interstitium. MWCNT exposure has been shown to induce fibrosis as early as seven days post-exposure [8, 10, 45]. In previous experiments, the post-exposure pulmonary distribution, pulmonary fibrotic response and transport of MWCNT to systemic organs were examined at various times post-exposure, from 1 to 336 days [46, 47]. Fibrillar collagen in the lungs was specifically stained and the quantity of fibrillar collagen in the alveolar region was measured by morphometry. These measurements of fibrillar collagen in the alveolar region of the lungs demonstrated a fibrotic response to inhaled MWCNT which was significantly above vehicle controls and progressively increased throughout the 336 days post-exposure study period . These studies have demonstrated that inhaled MWCNTs are deposited throughout the alveolar region of the lungs and are retained in the alveolar tissue. Additionally MWCNT were demonstrated in the visceral pleura, pleural space and parietal space . MWCNT that penetrate the visceral pleural induce pleural inflammation and cell proliferation in a manner similar to asbestos [8, 48, 49]. MWCNT have further been shown to penetrate the cytoplasmic membrane and nuclear envelope [50, 51].
Asbestos and MWCNT also induce inflammation, fibrosis, cell proliferation and cellular atypia in the lung [8, 48, 49]. Cell proliferation and inflammation are important events in the promotion of cancer [16, 17, 52–55]. Indeed in the current study, inhaled MWCNT induced dramatic hyperplasia and a moderate increase in adenomas however, the increase in adenomas was not statistically significant. In addition, MWCNT exposure did not result in an increased number of adenocarcinomas. The significant hyperplastic response that was observed after exposure to MWCNT material without prior initiation indicates that the material was a tumor promoter. The dramatic increase in adenomas and adenocarcinomas after MCA initiation followed by MWCNT-exposure demonstrate that inhaled MWCNT material is a strong tumor promoter. Strong tumor promoters increase the growth of chemically initiated as well as spontaneously initiated cells [56, 57]. Although the data of the current investigation do not indicate that inhaled MWCNT material act as tumor initiators, the data demonstrate the strongest promotion response observed in the lung using occupationally relevant material [15, 52, 58–60]. The data further indicate that MWCNT may initiate lung responses similar to the carcinogenic fiber asbestos [4, 61–63].
The dimensions of the nanotubes as well as their surface properties are important in the inflammatory response. Pulmonary exposure to SWCNT and MWCNT causes inflammation and fibrosis; however, the inflammatory response following MWCNT exposure is more pronounced than the response observed following SWCNT exposure [8, 64, 65]. The degree of inflammation resulting from asbestos and MWCNT is determined by the diameter and the length [4, 66, 67]. Carbon nanotubes of approximately 50 nm in diameter cause more inflammation than nanotubes of less than 20 nm or greater than 150 nm . In addition, the rigid MWCNT of 40–50 nm diameter and at least 4 microns long were the most inflammatory [67, 68]. Although these studies indicate that the diameter and length of carbon nanotubes may alter MWCNT-induced carcinogenicity further investigations are required to fully characterize the role of the dimensions as well as the physical properties in the carcinogenic response.
Classical multistep carcinogenesis models involve initiation, promotion and progression. Exposure to a genotoxic agent initiates a population of genetically altered cells which expand in number through the action of promoters and undergo additional genetic changes during the progression process [16, 17, 69]. Several studies suggest both genotoxicity and promotion from the classical carcinogenic high aspect ratio particle, asbestos. Oxidant generation from inflammation has been shown to damage the DNA and can initiate cancer . Asbestos and carbon nanotubes have been shown to induce disruption of the cell division apparatus and errors in chromosome number (aneuploidy) in vitro[12, 14, 70]. The long, thin asbestos fibers of less than 0.25 μm diameter and at least 5 microns in length are the most genotoxic [71, 72]. The mutagenicity of asbestos fibers is correlated with the potency as a carcinogen . Evidence from epidemiological studies has demonstrated that asbestos can act as a tumor promoter at low doses as well as a tumor initiator at longer and/or higher exposure levels . In several human epidemiology studies, smoking exposure and asbestos interact in a more than additive fashion in causing lung cancer [75–79]. There are multiple mutagens in cigarette smoke that have the potential to initiate cancer . Humans are also potentially exposed to many other mutagens that could initiate cancer such as radon, polychlorinated biphenyls, hexavalent chromium, naphthalene and benzo-a-pyrene in diesel exhaust [81–85]. Thus, it is plausible to suggest MWCNT could potentially act as promoters in individuals who smoke or are exposed to other initiators.
Previous studies to examine rodent exposure to asbestos by inhalation or pharyngeal aspiration have shown that asbestos is carcinogenic in the rat lung by this route but only weakly positive in the mouse [86–88]. The data demonstrating that asbestos induces mitotic spindle disruption and aneuploidy would suggest that asbestos would be a strong tumor promoter; however, asbestos has not been administered in an initiation/promotion protocol in a mouse model. Although lung cancer has not been observed in either rats or mice following the intraperitoneal injection of asbestos or carbon nanotubes, mesothelioma has been reported. Abdominal or scrotal injection of mice with asbestos or long thin MWCNT of at least 3.9 micron in length and 50 nm in diameter caused mesotheliomas in p53 +/- transgenic mice and Fischer rats [20, 21]. Recent investigations demonstrated that intraperitoneal injection of as little as 3 μg of MWCNT in genetically modified mice (p53+/-) induced mesothelioma . By contrast, an IP exposure of Wistar rats to short MWCNT of < 1 micron in length resulted in mesothelioma in 5/150 MWCNT-exposed animals but those findings were not statistically significant due to a high peritoneal mesothelioma rate in the control group . The high background rate of peritoneal mesotheliomas (1/26) is unusual for the Wistar rat [89–91]. A subsequent study demonstrated that high exposures (1 and 10 mg/rat) of thin, rigid MWCNT by intraperitoneal injection caused mesotheliomas (54). When the diameter of the nanotubes was considered, MWCNT of 50 nm in diameter were more carcinogenic than nanotubes of less than 20 nm or greater than 150 nm . These findings suggest that the diameter and length are critical in the carcinogenic response to MWCNT, a finding that is similar to classical studies of asbestos fiber carcinogenicity .
A limitation of the current study is that suitable non-carcinogenic particle controls do not exist in this model. We considered using the short multi-walled carbon nanotubes investigated by Muller et al., as a potential negative control . However, since the interpretation of the Muller et al. study is affected by the unusual high background rate of peritoneal mesothelioma in the control group, this particle cannot be considered a confirmed negative control nor could we identify any carbon nanotube as a confirmed negative particle control for a carcinogenicity study. The identification of a suitable negative control nanotube will require further carcinogenicity studies that have yet to be published.
Malignant mesothelioma in humans has three major histologic patterns: epithelial, sarcomatous (sarcomatoid), and biphasic [93, 94]. Using standard histopathology, the major differential diagnoses for malignant mesothelioma include broncho-alveolar adenocarcinoma of the lung, metastatic carcinoma and metastatic sarcoma . The diagnosis of malignant mesothelioma in humans can be supported by staining for proteins commonly expressed in mesotheliomas, including calretinin, cytokeratins, mesothelin, WT-1 and podoplanin (D2-40) . Podoplanin is among the markers most consistently expressed in human malignant sarcomatous mesotheliomas [34, 95]. The malignant serosal tumors seen in the mice in our study consistently expressed podoplanin. However, the staining for cytokeratins was negative to equivocal, a finding that is also sometimes seen in sarcomatous mesothelioma in humans [35, 36]. One review noted that only 13% of human sarcomatous mesotheliomas were positive for cytokeratin 5/6 and none were positive for seven other epithelial markers . However, in one study using a cocktail of mouse anti-human monoclonal antibodies, 93% of the cases of human sarcomatous mesotheliomas demonstrated cytokeratin expression . However, there are protein sequence differences between human and mouse cytokeratins. In addition, even with blocking steps, indirect immunohistochemistry using mouse antibodies on mouse tissues results in some degree of binding of the secondary anti-mouse IgG antibody with endogenous IgG located in the mouse tissue. It is for this reason that we used both a mouse monoclonal antibody and a rabbit anti-pancytokeratin antibody to stain for cytokeratins in this study. However, the negative to equivocal staining of the serosal tumors for cytokeratins in this study should be interpreted with an understanding that mesotheliomas are very rare in the mouse and that techniques for identifying mesothelioma markers in mice are not as advanced as they are for identifying those markers in human tissue. The negative staining does not mean that there are no cytokeratins in the serosal tumors of our study, only that no cytokeratins could be identified with the antibodies used in this study.
In humans, podoplanin staining in the absence of cytokeratin staining can be seen in several different sarcomas as well as in malignant mesothelioma [34, 97]. The malignant serosal tumors seen in this study were morphologically consistent with malignant sarcomatous mesotheliomas with five of the six tumors involving multiple peritoneal serosal surfaces. The remaining malignant serosal tumor was limited to the male urogenital tract, a common site for mesothelioma in rats but not in control mice . In humans, a diagnosis of cytokeratin negative sarcomatous mesothelioma is usually made by excluding other potential diagnoses . Given the rarity of mesotheliomas in the mouse, we could not exclude other diagnoses with absolute certainty . Thus, the characteristics of these tumors are consistent with, but not diagnostic of, mesothelioma. The principal differential diagnosis is pleural sarcoma.
These tumors are considered similar to the serosal tumors diagnosed as pleural sarcomas or malignant mesenchymal neoplasms in the classical asbestos studies in rats conducted by Stanton and co-workers who noted their comparability to human mesotheliomas .
This study is the first to demonstrate that inhalation exposure to some MWCNTs promotes the growth of initiated lung cells in a wildtype mouse. Ninety percent of the mice exposed to MCA followed by MWCNT had lung adenocarcinoma and adenomas (mean of 2.9/mouse) compared to 23% of the filtered air controls (mean of 0.25/mouse), 26.5% of the MWCNT-exposed (mean of 0.38/mouse), and 51.9% of the MCA followed by air-exposure (mean of 0.81/mouse). The data therefore demonstrate that inhaled MWCNT are strong promoters of pulmonary adenomas and adenocarcinomas in B6C3F1 mice. Furthermore, the strong tumor promotion response observed following exposure to MWCNT was observed in a hybrid mouse that is intermediate in sensitivity to lung cancer [25, 26]. Because this B6C3F1 hybrid is used by the NTP to determine potential carcinogenesis, the study can be compared to a wealth of historical data generated by the NTP .
Furthermore, the current investigation suggests that inhaled MWCNT can promote the growth of malignant serosal tumors consistent with sarcomatous mesothelioma. MWCNT inhalation increased the incidence from 2% in the MCA exposed mice to 9% in the MCA + MWCNT, a 4.5 fold increase. However, malignant serosal tumors are uncommon tumors in mice and their potential promotion by MWCNT is of concern. NIOSH is undertaking an inhalation exposure designed to further evaluate the potential for MWCNT to cause mesothelioma. The mouse MWCNT lung burdens in the investigation are relevant to feasible human occupational exposures. While extrapolation to human health is premature, humans working with MWCNT may be exposed to numerous tumor initiators in the course of their daily lives. Results from this study suggest that caution should be taken during production and processing to limit human inhalation exposures to MWCNT.
MWCNT used in this study were obtained from Hodogaya Chemical Company (Mitsui-7 MWNT-7, lot #061220-31) and were manufactured using a floating reactant catalytic chemical vapor deposition method followed by high temperature thermal treatment in argon at 2500°C using a continuous furnace . The bulk material was characterized by high-resolution transmission electron microscopsy under a Philips CM 20 transmission electron microscope (TEM) with an EDS (EDAX/4p1) as described previously . MWCNT trace metal contamination of 1.32% with iron being the major metal contaminant was 1.06% .
MWCNT inhalation exposure and aerosol characterization
The MWCNT aerosol was generated using an acoustical-based computer controlled whole body inhalation system designed and constructed by McKinney et al, . 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 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. Chen et al. have provided a detailed characterization of MWCNT samples taken from the animal exposure chamber . In addition, cascade impactors (MOUDI, Models 110 and 115, MSP Co., Shoreview, MN) were used to determine the mass-based particle size distributions by fractionating the particles into 15 size fractions ranging from 10 nm to 18 μm. The mass median aerodynamic diameter was determined to be 1.59 μm and geometric standard deviation of 1.69. The count mode aerodynamic diameter was 0.42 μm [101, 102]. The target concentration of the mouse exposure was 5 mg/m3 for a duration of 5 hours/day for 15 days, with an accumulative exposure dose of 375 mg/m3 × hr. The values of detailed exposure parameters were presented in Additional file 1: Table S1. Based on data from Data RAM and filter samples, the mean concentrations among the 5 exposures were consistent at 4.6-4.7 mg/m3 with a daily variation between 4–8%. Depending on the concentration measured daily, the exposure time was adjusted accordingly to result in the target dose of 375 mg/m3 × hr. The mean exposure time per day was 320–330 minutes with a daily variation between 1–3%. The accumulated dose was measured between 372 and 379 mg/m3 × hours and therefore was very close to the target dose of 375 mg/m3 × hr. In brief, the study was well conducted to fulfill the exposure design.
Initiation promotion protocol
Six week old male B6C3F1 mice (Jackson Laboratories, Bar Harbor, ME) were housed singly in a polycarbonate ventilated cage with HEPA-filtered air. Male mice were selected for the investigation because the preliminary data showing dose response, proliferation of type II cells, cellular atypia and migration of particles following carbon nanotube exposure were gathered using male mice [7–9, 103]. The mice were fed ad libitum with Harlan 7913 irradiated NIH-31 modified 6% rodent chow. The initiation, promotion protocol developed previously by Alvin Malkinson was followed . After a one week acclimation period, mice (60/group) were randomly assigned to a treatment group. The mice were treated following a two stage (initiation-promotion) protocol. An initiation-promotion protocol involved the administration of a low dose of a DNA damaging agent (methylcholanthrene, MCA) followed by administration of a suspected carcinogen that would promote the growth of DNA damaged cells (MWCNT). All mice received a single dose of either MCA (10 μg/g BW, i.p.) or vehicle (corn oil). One week after receiving MCA, mice were exposed to MWCNT by whole body inhalation (5 mg/m3, 5 hours/day) or filtered air (controls) for 15 days. Mice were euthanized 17 months after exposure to allow time for tumor development. Mice were divided into five blocks with staggered test substance administration start and end dates.
Because animals developing lung tumors have non-specific symptoms but may develop general signs of pain and distress, animals were monitored weekly for overt signs of morbidity and changes in body weight. Animals with skin lesions, ruffled fur, lethargy, shaking, penis or anal prolapse, erratic movements or paralysis were closely monitored for further signs of distress. Animals that had a loss of 20% or greater of body weight, were hunched or developed hind leg paralysis were euthanized for morbidity prior to the terminal sacrifice.
Foreign material in lung tissues
MWCNT burden determinations were made using a procedure previously developed with minor modification . After euthanasia, lungs were removed and frozen at -80°C and preserved for further processing. The lung tissue was digested in 25% KOH/methanol (w/v) at 60°C overnight, followed by centrifugation at 16,000 × g for 10 minutes. The supernatant was removed; the remaining pellet was mixed with 50% HNO3/methanol (v/v), and incubated at 60°C overnight, followed by centrifugation (16,000 × g, 10 minutes). After centrifugation, the supernatant was removed, and the pellet was resuspended in 10% NP-40 (v/v) in dH2O, followed by 30 second sonication using cup horn sonicator. MWCNT standards were processed in parallel with the lung samples. The optical densities of the solutions were measured at 700 nm using a UV/visible spectrophotometer. Lung MWCNT content was determined from a standard curve.
Necropsy, histopathology and tumor counts
Groups of mice were divided into five blocks with staggered test substance administration start and end dates. The lungs and any masses from mice euthanized early were noted and the tissues collected for pathological analysis. The mice euthanized early, due to signs of morbidity , were analyzed separately from animals that were sacrificed 17 months after exposure. Mice were euthanized with an overdose of ≥100 mg/kg bw pentobarbital and exsanguinated. The lungs were fixed by intratracheal perfusion with 1 ml of 10% neutral buffered formalin. The mice were then necropsied following standard techniques . Masses and lesions seen grossly were recorded on individual animal necropsy records (IANRs). The length, width and height of masses were measured in the MCA, air, MWCNT and MCA + MWCNT-treated mice, using a digital caliper. The calculations of the tumor volumes for spherical masses were done using (4/3 π)(r3) and for non-spherical masses (Length × Width × Height). All gross lesions and masses were then collected and fixed in 10% neutral buffer formalin (NBF). Lungs and any lesions were trimmed the same day and processed overnight. Tissues were embedded in paraffin, and sectioned at approximately 5 μm. Hematoxylin and eosin (H & E) stained slides were prepared each of the five separate lung lobes and from masses seen at necropsy. The tumor counts were based on histopathological analysis.
Slides were examined by a board certified veterinary pathologist using light microscopy or polarized light, which was occasionally used to confirm the presence or absence of foreign material (presumptive test material). The severity of non-neoplastic lesions was graded on a 4-point scale of minimal (1), mild (2), moderate (3), or marked (4) using an adaptation of previously described methods . Presumptive MWCNT (foreign material) was recorded when present without severity grade . Focal adenomatous alveolar hyperplasia was characterized by increased numbers of crowded alveolar epithelial cells that outlined contiguous alveolar septa in discrete, generally random locations (Figure 3). Severity was considered minimal, mild, moderate, or marked if roughly <5, 5–10, 11–20, or >20 contiguous alveoli were affected, respectively. Severity was increased or decreased a grade based on cell density and crowding. Histologic diagnoses were entered into the Provantis® data collection and management system. All lung slides from 10% of the mice in the terminal sacrifice were randomly selected for evaluation by a second board-certified veterinary pathologist who independently evaluated the slides while blinded to the interpretation of the study pathologist. There was 100% concordance on the diagnosis of neoplasia and 87% concordance on the diagnosis of adenocarcinoma versus adenoma. The differences were in the diagnosis of adenocarcinoma versus adenoma were considered by both the peer review and study pathologist to involve borderline lesions where such differences would be expected.
Tumor multiplicity (Table 2) was analyzed two ways. First, the number of tumors was divided by the number of animals that had tumors in each treatment group and was labeled “mean # of lung tumor per mice with tumors”. Secondly, the multiplicity was determined by dividing the number of tumors by the number of animals in the treatment group and was labeled “lung multiplicity adjusted by the total number of mice” (Table 2).
Immunofluorescent detection of markers for mesothelioma
Immunofluoresecent staining for mesothelial proteins were performed on sarcomatous tumors of the peritoneal and epididymal surface in mice exposed to both MWCNT and MCA. Proteins identified by immunofluorescence were cytokeratins (wide spectrum), vimentin and podoplanin based upon their previously described expression in mouse or human mesothelioma [34, 105–107]. To localize sites of vimentin and podoplanin expression to sites of cytokeratin expression, the immunofluorescence staining used double labeling for: 1) cytokeratin and vimentin, and 2) cytokeratin and podoplanin. Immunofluorescence was selected because it is more sensitive for identifying fluorescence in long, thin cytoplasm such as in alveolar type I cells or normal mesothelial cells .
For immunofluorescent staining, slides were deparaffinized, antigenicity was retrieved using EDTA, and non-specific reactivity was blocked with normal donkey serum (017-000-121, Jackson ImmunoResearch Laboratories, West Grove, PA), as previously described . Two primaries from different species were used for each double label. Primary antibodies were hamster anti-podoplanin (NB600-1015, Novus Biologicals, Littleton, CO), mouse anti-pancytokeratin (C2652, Sigma-Aldrich, St Louis, MO), rabbit anti-vimentin (GTX62264, GeneTex, Irvine, CA), and rabbit anti-wide spectrum cytokeratin (rabbit ab9377). Secondary anti-bodies were DyLight 488, donkey anti-mouse (715-486-150, lot# 97733, Jackson ImmunoResearch Laboratories, West Grove, PA), DyLight 594 goat anti-hamster (107-515-142, lot 90054, Jackson ImmunoResearch Laboratories, West Grove, PA), Dylight 488 F(ab’)2 donkey anti-rabbit and DyLight 594 donkey anti-rabbit (711-516-152, lot 97356, Jackson ImmunoResearch Laboratories, West Grove, PA). Nuclei were stained using DAPI Fluoro Pure and slides were cover slipped with Prolong anti-fade reagent. Negative control slides were treated identically except that the primary antibody was replaced with non-immune serum from the same species as the primary antibody. Positive control slides were the normal mesothelial lining of the liver and lung.
Enhanced-darkfield light microscopy imaging of nanoparticles
Carbon nanotubes in sections from exposed lungs were assessed using an enhanced-darkfield optical system as previously described . 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 and are visible with high contrast when examined with an enhanced-darkfield optical system designed to image scattered light in the section.
The optical system 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 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 hematoxylin and eosin, sections were coverslipped with Permount. After alignment of the substage oil immersion optics with a 10× objective, sections were examined with 60× air or 100× oil immersion objectives. Enhanced darkfield images were taken with a 2048 × 2048 pixel digital camera (Dage-MTI Excel digital camera XLMCAT, Michigan City, In 46360).
All analyses were performed using SAS/STAT version 9.3 for Windows. Binary outcomes of tumor incidence (tumor or not) for each type and for the total were analyzed using Fishers Exact test. Tumor counts were analyzed using Poisson regression for total tumor counts. In cases where Poisson regression demonstrated overdispersion a negative binomial regression was used. All analyses were stratified by promoter. Using the Proc Lifetest procedure in SAS, the log-rank test gave a p-value of 0.1609 for any differences among the 4 treatment groups with respect to the survival curves. Stratifying by initiator, the p-value with respect to the difference between MWCNT and Air was 0.3055, and 0.1288 for the corn oil and MC treated animals respectively.
Research findings and conclusions are those of the authors and do not necessarily represent the views of the National Institute for Occupational Safety and Health.
This work was supported by a Grant-in-Aid for Specially Promoted Research from the Ministry of Education, Culture, Sports, Science and Technology of Japan (MEXT) (No. 19002007) (ME), the Exotic Nanocarbon Project, Japan Regional Innovation Strategy Program by the Excellence, JST (Japan Science and Technology Agency) (ME, ST) The authors would like to thank Ms. Kim Clough Thomas, National Institute for Occupational Safety and Health, Morgantown, WV 26505 for her assistance with the figures.
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