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In vivo genotoxicity assessment of a multiwalled carbon nanotube in a mouse ex vivo culture

Genes and Environment volume 44, Article number: 24 (2022) Cite this article

Abstract

Background

Multiwalled carbon nanotubes (MWCNTs) are suspected lung carcinogens because their shape and size are similar to asbestos. Various MWCNT types are manufactured; however, only MWNT-7 is classified into Group 2B by The International Agency for Research on Cancer. MWNT-7’s carcinogenicity is strongly related to inflammatory reactions. On the other hand, inconsistent results on MWNT-7 genotoxicity have been reported. We previously observed no significant differences in both Pig-a (blood) and gpt (lung) mutant frequencies between MWNT-7-intratracheally treated and negative control rats. In this study, to investigate in vivo MWNT-7 genotoxicity on various endpoints, we attempted to develop a lung micronucleus assay through ex vivo culture targeting the cellular fraction of Clara cells and alveolar Type II (AT-II) cells, known as the initiating cells of lung cancer. Using this system, we analyzed the in vivo MWNT-7 genotoxicity induced by both whole-body inhalation exposure and intratracheal instillation. We also conducted an erythrocyte micronucleus assay using the samples obtained from animals under intratracheal instillation to investigate the tissue specificity of MWNT-7 induced genotoxicities.

Results

 We detected a significant increase in the incidence of micronucleated cells derived from the cellular fraction of Clara cells and AT-II cells in both MWNT-7-treated and positive control groups compared to the negative control group under both whole-body inhalation exposures and intratracheal instillation. Additionally, the erythrocyte micronucleus assay detected a significant increase in the incidence of micronucleated reticulocytes only in the positive control group.

Conclusions

Our findings indicated that MWNT-7 was genotoxic in the lungs directly exposed by both the body inhalation and intratracheal instillation but not in the hematopoietic tissue.

Background

Fibrous or rod-shaped micrometer length particles, which share dimensions with asbestos, are carcinogenic [1,2,3,4,5]. Since the properties of multiwalled carbon nanotubes (MWCNTs) are similar to asbestos, MWCNTs are suspected as carcinogenic in the lung. Although various types of MWCNTs with different particle sizes and specific surface area are manufactured, only MWNT-7 (although shown as “MWCNT-7” in the reference [6], “MWNT-7” is correct), has been classified as “possibly carcinogenic to human (Group 2B)” by The International Agency for Research on Cancer (IARC) [6].

There are several conflicting reports on the in vivo genotoxicity of MWNT-7 (Table 1). Intratracheal MWNT-7 instillations were genotoxic to mice as demonstrated by comet assays using lung cells [7] and bronchoalveolar lavage (BAL) cells [8]. Both single pharyngeal aspiration and inhalation exposure with MWNT-7 were genotoxic to mice in comet assays using lung cells and BAL cells [9]. Interestingly, the inhalation exposure of MWNT-7 induced a higher incidence of micronucleated cells on alveolar Type II (AT-II) cells than the negative control, which supposedly represent the target cells of lung cell carcinogenesis [9]. On the other hand, lacZ mutant frequency analysis using lung samples collected from female MutaTMMouse 60 days after the final treatment revealed that intratracheal MWNT-7 instillations were not genotoxic [10]. Additionally, we had previously reported that MWNT-7 administered intratracheally to male rats was negative in both the Pig-a assay using blood and the gpt assay using lungs collected 28 days after the single treatment [11].

Table 1 Summary of in vivo genotoxicities and experimental conditions in MWNT-7-studies
Full size table

These discrepancies on MWNT-7 genotoxicity prompted us to examine in vivo genotoxicity at different endpoints from our previous study. Here, we attempted to develop a lung micronucleus assay through ex vivo cell culture to increase cell division targeting the cellular fraction of Clara cells and AT-II cells, known as the primordial cells of lung cancer [9, 14]. Using this test system, we analyzed MWNT-7 in vivo genotoxicity induced by both whole-body inhalation exposure and intratracheal instillation. Additionally, we conducted an erythrocyte micronucleus assay under intratracheal instillation to investigate the tissue specificity of MWNT-7-induced genotoxicity.

Results

Under whole-body inhalation exposure

We conducted the first experiment with a small number of mice per dose group, followed by the confirmatory studies with more mice per dose group. Ethyl methane sulfonate (EMS) was intraperitoneally administered as a positive control.

Typical micronucleated cells induced by ex vivo culture are shown in Fig. 1. In the first test using a small number of mice per dose group, the incidence of micronucleated cells increased significantly in the MWNT-7- and EMS-treated groups compared with the negative control [mean ± SD (%) for mice treated with air, 0.283 ± 0.076; MWNT-7, 1.483 ± 0.548; EMS, 0.567 ± 0.126] (Fig. 2A). In the confirmatory test, the incidence of micronucleated cells also increased significantly in the MWNT-7- and EMS-treated groups [mean ± SD (%) for mice treated with air, 0.390 ± 0.119; MWNT-7, 1.330 ± 0.449; EMS, 0.820 ± 0.114] (Fig. 2B).

Fig. 1
figure 1

Examples of typical micronucleated cells in the MWNT-7-treated group. The prepared slide specimens were stained with a mixture of acridine orange (AO, 500 µg/ mL) -4′, 6-Diamidino-2-phenylindole (DAPI, 10 µg/ mL). The specimens were observed under a fluorescent microscope at 400× magnification with U-excitation (ultraviolet ray excitation, wave length: 330–385 nm). Micronucleated (MN) cells are shown by arrows identified as “MN.”

Full size image
Fig. 2
figure 2

Results of the lung micronucleus assay through ex vivo culture after whole-body inhalation exposure. Left (A) and right (B) panels show the results of the first and confirmatory tests, respectively. The Y-axis indicates the incidence of micronucleated (MN) cells. Each treatment group is shown under the bars. The data correspond to the mean ± SD. * p< 0.05 compared to the control (Fisher’s exact test).

Full size image

Under intratracheal instillation

Since we detected clear positive results in the lung micronucleus assay under whole-body inhalation exposure, we conducted the experiments under intratracheal instillation to investigate genotoxic effects caused by the different exposure methods to lung. Additionally, we conducted an erythrocyte micronucleus test to analyze the tissue specificity of MWNT-7-induced genotoxicity.

Although the erythrocyte micronucleus assay detected a significant increase in the incidence of micronucleated reticulocytes only in the positive control group [mean ± SD (%) for mice treated with only vehicle, 0.448 ± 0.060; MWNT-7, 0.418 ± 0.026; EMS, 2.210 ± 0.319] (Fig. 3A), significant increases in the incidence of lung micronucleated cells in both MWNT-7 treated and positive control groups were detected [mean ± SD (%) for mice treated with only vehicle, 1.403 ± 0.457; MWNT-7, 3.517 ± 0.808; EMS, 4.348 ± 0.936] (Fig. 3B).

Fig. 3
figure 3

Results of the erythrocyte (A) and the lung (B) micronucleus assays through ex vivo culture after intratracheal instillation. The Y-axis indicates the incidence of micronucleated (MN) cells. Each treatment group is shown under the bars. The data correspond to the mean ± SD. * p< 0.05 compared to the control (Fisher’s exact test).

Full size image

Discussion

MWCNTs are classified based on its characteristic size and surface areas. Among these groups, only MWNT-7 has been categorized as “possibly carcinogenic to humans (Group 2B)” by the IARC based on various evidence [4,5,6, 15,16,17]. Recently, Moller et al. reviewed the genotoxicity of MWCNTs including MWNT-7 with conflicting results with respect to MWNT-7 in vivo genotoxicity [18]. We here summarized these conflicting results and experimental conditions in detail (Table 1).

According to several reports, comet assays targeting the lungs were positive in all but one case [7,8,9,10]. In these positive cases, the lungs were collected shortly after MWNT-7 treatment, regardless of the exposure route e.g., inhalation exposure, pharyngeal instillation, or intratracheal instillation (Table 1) [7,8,9]. We here attempted to develop a lung micronucleus assay through ex vivo culture targeting the cellular fraction of Clara cells and AT-II cells [9, 14]; we found positive results under both whole-body inhalation exposure and intratracheal instillation (Fig. 2 and 3). In the present case, we collected the lungs 5 or 2 days after whole-body inhalation exposure or intratracheal instillation, respectively.

On the other hand, in the negative case in the comet assay and the negative lacZ mutant frequency analysis, the lungs were collected 60 days after the final treatment [10]. We had previously reported that MWNT-7 administered intratracheally to male rats was negative in the gpt assay using lungs collected 28 days after a single treatment [11]. From these indications, in analyses targeting the lung, except one case in the gpt assay [7], it seems that MWNT-7 genotoxicity was negative when sampling times were much later than the final administration e.g., 28–60 days, but positive otherwise e.g., 3 h–5 days. Therefore, we suspected that this time difference may have influenced these results, rather than differences in exposure routes.

MWNT-7 inhalation exposure was negative in the micronucleus test using bone marrow [9]. Additionally, the standard erythrocyte micronucleus test revealed no genotoxicity of oral MWNT-7 gavage [12]. We reported a negative result in the Pig-a assay using blood samples collected 28 days after a single intratracheal treatment on male rats [11]. Here, we showed negative MWNT-7 genotoxicity in the erythrocyte micronucleus test (Fig. 3A). From these findings, it appears that the genotoxic effects of MWNT-7 are not systemic.

The carcinogenicity and toxicity induced by exposure to nanomaterials are strongly related to inflammatory reactions and reactive oxygen species [19,20,21,22,23]. Additionally, in case of MWCNTs, these effects are related to MWCNT dose, time, and physicochemical properties [24]. Interestingly, the incidence of lung micronucleated cells in the negative control group under intratracheal instillation was slightly higher than under whole-body inhalation exposure (Fig. 2 and 3B). Only air was supplied to the negative control group under whole-body inhalation exposure whereas saline containing 0.1% Tween-80 was used to treat the negative control group under intratracheal instillation. Therefore, a slight inflammatory reaction may have occurred under intratracheal instillation which slightly increased the incidence of lung micronucleated cells observed under these conditions.

All these studies indicate that exposure conditions, method, route, sampling time, and endpoints are important when evaluating MWCNT genotoxicity. Here, we showed that MWNT-7 was genotoxic in lungs directly exposed by both whole-body inhalation exposure and intratracheal instillation, although MWNT-7 was not genotoxic in the hematopoietic tissue. From our results, we still cannot explain the mechanism(s) of MWNT-7-induced in vivo genotoxicity; however, it is strongly suspected that this mechanism(s) is correlated with the local response at the tissue directly exposed to MWNT-7.

Conclusions

We developed a lung micronucleus assay through ex vivo cell culture targeting on cellular fraction of Clara cells and AT-II, and analyzed MWNT-7 genotoxicity under whole-body inhalation and intratracheal instillation. Additionally, we conducted an erythrocyte micronucleus assay under intratracheal instillation. With respect to MWNT-7 genotoxicity, we detected a positive result in the lung micronucleus assay. Our findings indicated that MWNT-7 was genotoxic in the lungs directly exposed by both the body inhalation and intratracheal instillation, but not in the hematopoietic tissue.

Methods

Animals

C57BL/6NcrSlc male mice were obtained from Japan SLC (Shizuoka, Japan). Administrations were started in mice at 12-weeks-old. The animals were housed individually under specific pathogen-free conditions with a 12-h light–dark cycle. Food (CRF-1 pellet feed, Oriental Yeast Co., Ltd., Tokyo, Japan) and water were available ad libitum. Animal experiments were conducted in accordance with the regulations of the Animal Care and Use Committees of the National Institute of Health Sciences (approval protocol No. 693, 730, and 763).

Test chemicals

MWNT-7 (Lot No. 060125-01k, Mitsui & Co., Ltd., Ibaraki, Japan) was prepared as described previously [4, 5, 11, 25]. Accordingly, MWNT-7 fibers are approximately 100 nm in diameter, and 27.5% of the MWCNTs are ≥5 μm in length. MWNT-7 was treated by the Taquann method to obtain well-dispersed MWNT-7 without aggregation/agglomeration [13]. EMS (Sigma-Aldrich Corporation) was dissolved in physiological saline at 2.5 and 20 mg/mL.

Dose levels and treatments for whole-body inhalation exposure

Three or five male mice per treatment group were used for the first or confirmatory tests, respectively. The dose and administration period that had been confirmed to provide sufficient lung exposure to MWNT-7 in the previous report were applied in this study [13]. For MWNT-7-treated groups, mice were exposed to MWNT-7 at 2 mg/m3 for 2 h/day for five consecutive days, with systemic inhalation using Taquann Direct-Injection Whole Body Inhalation System version 2.0 [13]. For the negative control groups, mice were exposed to air in an analogous manner. EMS was intraperitoneally administered at 25 mg/kg/day at 24-h intervals for 5 consecutive days as positive controls. At 5 days after the final dosing, the animals were exsanguinated via the abdominal aorta under anesthesia and the lungs were sampled.

Dose levels and treatments for intratracheal instillation

Six male mice per treatment group were used. A MWNT-7 suspension was prepared as described previously [26]. The dosing conditions to provide sufficient lung exposure to MWNT-7 were determined according to the previous reports, with some modifications [7, 26]. Briefly, Taquann method-treated MWNT-7 was dispersed into a physiological saline solution containing 0.1% Tween-80 at 0.5 mg/mL, and sonicated using an ultrasound bath for 30 min immediately before administration. Next, mice were intratracheally injected with vehicle (saline containing 0.1% Tween-80) or 0.05 mg/animal weight of MWNT-7. EMS was intraperitoneally administered at 200 mg/kg body weight/day at 24-h intervals for two consecutive days as positive controls. At 48 h (vehicle or MWNT-7 treated groups) or 24 h (EMS-treated group) after the final dosing, the animals were exsanguinated via the abdominal aorta under anesthesia and the blood and lungs were sampled.

Lung micronucleus assay through ex vivo culture

The lung micronucleus assay through ex vivo culture was performed as previously described with some modifications [9, 14]. Briefly, the cellular fraction of Clara cells and AT-II cells was isolated by centrifugation in a Percoll gradient, and the isolated cells were incubated at 37˚C for 48 h. After culturing, cells were collected and treated with 1% sodium citrate solution for hypotonic treatment. Hypotonic treated cells were fixed with an acetic acid-ethanol (1: 3) fixation solution to prepare slide specimens. These specimens were stained with a mixture of acridine orange (AO, 500 µg/mL) -4′,6-diamidino-2-phenylindole (DAPI, 10 µg/mL), and observed under a fluorescent microscope at 400× magnification with U-excitation (ultraviolet ray excitation, wavelength: 330–385 nm). Relatively large round to oval cells were used as target cells (Clara cells and AT-II cells), and cells that could be identified as leukocytes were excluded from the observation target. About 2,000 cells/animal or 1,000 cells/animal from each treatment group of the whole-body inhalation exposure or intratracheal instillation, respectively, were counted and the incidence of lung micronucleated cells was calculated. Differences in the incidence of micronucleated cells in treatment groups vs. negative controls were analyzed by 2-tailed Fisher’s exact test.

Erythrocyte micronucleus test

The erythrocyte micronucleus test was performed using the MicroFlow Plus Kit (Litron) according to manufacturer’s instructions. Briefly, blood samples were fixed with methanol below -80˚C. The samples were stained with anti-CD61 antibody (staining platelets), anti-CD71 antibody (staining reticulocytes), and/or DNA staining solution, respectively. The incidence of micronucleated reticulocytes was calculated by measuring about 20,000 reticulocytes/animal using a flow cytometer. Differences in the incidence of micronucleated cells vs. negative control groups were analyzed by 2-tailed Fisher’s exact test.

Availability of data and materials

All data generated or analyzed during this study are included in this published article.

Abbreviations

MWCNT:

multiwalled carbon nanotube

AT-II:

alveolar Type II

EMS:

ethyl methane sulfonate

AO:

acridine orange

DAPI:

4′, 6-Diamidino-2-phenylindole

U-excitation:

ultraviolet ray excitation

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Acknowledgements

We gratefully acknowledge Tomoko Ando, Kensuke Satomoto, Atsushi Wakita, and Maki Nakamura for their technical help. This work was supported by Health and Labor Sciences Research Grant, Japan, Grant Number: H27-Chemical-Designation-004 and H30-Chemical-Designation-004.

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Authors and Affiliations

  1. Division of Genetics and Mutagenesis, National Institute of Health Sciences, 3-25-26 Tonomachi, Kawasaki-ku, Kawasaki-shi, Kanagawa, 210-9501, Japan

    Katsuyoshi Horibata, Kei-ichi Sugiyama & Masamitsu Honma

  2. LSIM Safety Institute Corporation, 14-1 Sunayama, Kamisu-shi, Ibaraki, 314-0255, Japan

    Hironao Takasawa, Miyuki Shigano & Shuichi Hamada

  3. Department of Pharmaceutical and Environmental Sciences, Tokyo Metropolitan Institute of Public Health, 3-24-1 Hyakunincho, Shinjuku, Tokyo, 169-0073, Japan

    Motoki Hojo

  4. Division of Cellular and Molecular Toxicology, National Institute of Health Sciences, 3-25-26 Tonomachi, Kawasaki-ku, Kawasaki-shi, Kanagawa, 210-9501, Japan

    Yuhji Taquahashi & Satoshi Yokota

  5. Division of Environmental Chemistry, National Institute of Health Sciences, 3-25-26 Tonomachi, Kawasaki-ku, Kawasaki-shi, Kanagawa, 210-9501, Japan

    Norihiro Kobayashi

  6. Division of General Affairs, National Institute of Health Sciences, 3-25-26 Tonomachi, Kawasaki-ku, Kawasaki-shi, Kanagawa, 210-9501, Japan

    Masamitsu Honma

  7. BoZo Research Center Inc, 1-3-11 Hanegi, Setagaya-ku, Tokyo, 156-0042, Japan

    Shuichi Hamada

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  1. Katsuyoshi Horibata
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Contributions

MH, YT, SY, and NK prepared MWNT-7 samples. YT conducted the inhalation experiments. MH conducted the intratracheal instillation. KH, HT, and MS conducted micronucleus assays using the lung cells and collected data. KH, SH, MH, HT, YT, KS, and MH designed and critically discussed the study. KH and SH have created the final manuscript. All authors read and approved the final manuscript.

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Correspondence to Katsuyoshi Horibata or Shuichi Hamada.

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Animal experiments were conducted in accordance with the regulations of the Animal Care and Use Committees of the National Institute of Health Sciences.

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Horibata, K., Takasawa, H., Hojo, M. et al. In vivo genotoxicity assessment of a multiwalled carbon nanotube in a mouse ex vivo culture. Genes and Environ 44, 24 (2022). https://doi.org/10.1186/s41021-022-00253-2

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Genes and Environment

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