Mutagenesis, Vol. 16, No. 3, 183-187,
May 2001
© 2001 UK Environmental Mutagen Society/Oxford University Press
Micronucleus induction and chromosomal aberration of 1- and 3-nitroazabenzo[a]pyrene and their N-oxides
Fukuoka Institute of Health and Environmental Science, Dazaifu, Fukuoka, Japan, 1 National Institute of Health Sciences, 1-18-1 Kamiyoga, Setagaya-ku, Tokyo, Japan and 2 Department of Environmental Health Science, Kyushu Women's University, Jiyugaoka Yahatanishiku, Kitakyushu, Japan
| Abstract |
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Nitro-azabenzo[a]pyrenes, 1- or 3-nitro-azabenzo[a]pyrene and their N-oxides are nitrated derivatives of azabenzo[a] pyrene (ABP) containing nitrogen in the 6-position of benzo[a]pyrene (B[a]P). The nitro-ABP-N-oxides (ABPOs) were formed by reaction of ABP with excess HNO3. These derivatives were noteworthy as potent mutagens for Salmonella strains, and were present in fine particles of diesel particulates. In this study, micronucleus induction in mice and chromosomal aberrations due to means of Chinese hamster lung fibroblast (CHL) cells were investigated to determine genotoxicity in order to define the relationship with the mutagenic potency of these derivatives. The induction of micronucleus polychromatic erythrocytes (MNPCEs) was dependent on the dose response of 1040 mg for 3-N-6-ABP, and of 1040 mg for 1-N-6-ABP, and in addition, 1- and 3-N-6-ABPOs markedly induced MNPCEs in a dose range of 10400 mg and from 1 to 80 mg, respectively, when the compound was intraperitoneally administrated in two mice at each dose. The results show that of the four compounds, 3-N-6-ABPO demonstrated a marked increase in MNPCEs. On the other hand, chromosomal aberrations of the four compounds were investigated by the duplicate tests using CHLs. The results after a 48 h treatment induced aberrations of the chromatid type, chromatid breaks and exchanges for 1- and 3-N-6-ABP, and mainly chromatid exchanges for 1- and 3-N-6-ABPO. The frequency of chromosomal aberrations associated with nitro substitution on the ABPO structure. Chromosomal aberrations of nitro derivatives of ABPO substituted at the 3-position on the structure were more potent than those at the 1-postion. N-oxide derivatives have been found to be reduced to anion radicals much more easily than azaB[a]P and its nitro derivatives. This suggests that the electrochemical reduction of the chemicals plays an important role in the metabolic activation of nitrated B[a]P derivatives.
| Introduction |
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The mutagenicity and genotoxicity of various polycyclic aromatic hydrocarbons (PAHs) and their nitrated derivatives have been widely investigated for bacterial and mammalian cells (Tokiwa et al., 1986), but those of azabenzo[a]pyrene (ABP) and its N-oxide derivatives containing nitrogen in the parent compound have not been clarified. According to our previous results, nitrated ABP and its N-oxides were found to be potent mutagens as well as nitrated derivatives of most PAHs for Salmonella tester strains (Sera et al., 1992
It has been reported that particulate air pollution was associated with lung cancer mortality and cardiopulmonary, and in particular, exposure to fine particles in air pollutants resulted in increased mortality and an increase in respiratory symptoms and respiratory hospitalizations (Pope et al., 1995
). Of the various mutagens present in fine particles, nitrated ABP and its N-oxides may play an important role in mutagenesis in lung cells and also may be associated with declines of lung function because the chemicals are more mutagenic and genotoxic than other nitroarenes.
In the present study, the genotoxic activity of 1- and 3-N-6-ABP or ABPO were determined for induction of micronuclei in polychromatic erythrocytes in mice, and chromosomal aberrations in Chinese hamster lung fibroblast (CHL) cells.
| Materials and methods |
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Chemicals
1- and 3-N-6-ABP and 1- and 3-N-6-ABPO were synthesized according to the methods mentioned in a previous report (Fukuhara et al., 1992
Micronucleus induction in mice
Eight-week-old ddY mice were used for determination of micronuclei. The animals were intraperitoneally treated with the test chemicals suspended in olive oil or dimethylsulfoxide (DMSO) at dose levels of 10150 mg/kg for 1- and 3-N-6-ABP, and 25400 mg/kg and 350 mg/kg for 1- and 3-N-6-ABPO, respectively. Twenty four hours after inoculation the animals were then killed by cervical dislocation. The test was replicated with the same age mice, and the mean results were calculated. The femoral marrow cells were flushed out with fetal bovine serum and smeared on clean slides. Some of the smeared cells were fixed with methanol for 5 min and stained according to the MayGrünwaldGiemsa technique. Other preparations were stained with acridine orange. The acridine orange (0.24 mM in 1/15 M of Sörensens phosphate buffer pH 6.8) was used as a working solution. The fixed slides were rinsed in the buffer three times for 13 min each time. The preparations were mounted with the same buffer, and sealed with Balsam paraffin or another suitable medium. Observations were made within 24 h. The slides were analyzed by one microscopist from coded slides; 1000 polychromatic and normochromatic erythrocytes with or without micronuclei were scored per animal. The ratio of polychromatic to normochromatic cells was simultaneously recorded by counting the number of cells until the score for one cell type reached 1000.
Chromosomal aberration test in vitro
The chromosomal aberration test was carried out according to the protocol previously reported by Matsuoka et al. (1991, 1993). Briefly, CHLs were cultured in Eagle's minimal essential medium (EMEM; Gibco BRL) supplemented with 10% heat-inactivated calf serum. In the direct method, cells were seeded at a density of 2.2x104 cells per dish with 5 ml of medium. On the third day, the cells were treated with each compound for 6, 24, or 48 h and then harvested. In the metabolic activation method, the cells were treated for 6 h with 0.5 ml of rat liver S9 mix, 2.5 ml of medium and 0.015 ml of the test compound dissolved in DMSO, 3 days after seeding. The final S9 concentration was 5%. The S9 fraction, prepared from the livers of male SD rats pretreated with phenobarbital and 5,6-benzoflavone, was purchased from Kikkoman. After the treatment, the reaction mixture was replaced with fresh medium and cells were harvested after an additional culture for 18 h. Chromosome preparation cultures were made and stained with Giemsa solution. The test was repeated three times and the data were summarized as the mean number of chromosome aberrations.
The slides were coded, but not scored, blind. One observer scored for aberrations. The number of cells with chromosomal aberrations among 100 well-spread metaphases was recorded. The types of aberrations were divided into six groups: chromatid and chromosome gaps (ctg), chromatid breaks (ctb), chromatid exchanges (cte), fragmentation (frg), chromosome breaks (csb) and chromosome exchanges (cse). In our criteria, a gap was a chromatic lesion whose length was longer than or equal to the width of a chromatid, suggesting a discontinuity at the DNA level. Thus, the evaluation of results was carried out including gaps in the present study. The incidence of polyploid cells among the 100 metaphases was also recorded. Solvent-treated cells served as negative controls.
Our historical database showed that the frequency of CHL cells with structural or numerical aberrations in both untreated and solvent-treated negative controls did not exceed 4%. We therefore decided a result was positive (+) if the frequency of aberrant cells or polyploidy was ~2-fold greater than that of the control, that is,
10%. The uncertain range between negative and positive, i.e. 59%, we termed inconclusive (±). Overall evaluation for each chemical was made by judging individual results in different dose groups. When the outcome was evaluated as inconclusive, the experiment was repeated.
Statistical analysis was conducted using the CochranArmitage test.
| Results |
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Incidence of micronucleus polychromatic erythrocytes (MNPCEs) with 1- and 3-N-6-ABP, and 1- and 3-N-6-ABPO
The chemical structures of 1- 3-N-6-ABP, and 1- 3-N-ABPO are illustrated in Figure 1
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Chromosomal aberrations of 1- and 3-N-6-ABP or ABPO
Chromosomal aberration tests for 1- and 3-N-6-ABP or ABPO were carried out using the direct method for 6, 24 and 48 h, and the results after 48 h of treatment are summarized in Tables I and II
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| Discussion |
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In this study, the results of micronucleus induction in mouse femoral marrow cells and chromosomal aberrations in CHLs showed the same structureactivity relationship for nitro-substitution of B[a]P, as in the results for Salmonella mutagenicity (Sera et al., 1992
On the other hand, chromosomal aberrations of nitro azaB[a]P and its N-oxides were mainly observed as chromatid breaks and exchanges. These aberrations were similar to the results for 3,7and 3,9-dinitrofluoranthenes (Tokiwa et al., 1988
). However, chromosome aberrations of nitro azaB[a]P and its N-oxides were not dependant on metabolic activation of rat liver S9 preparation whereas those of B[a]P were significantly induced in the presence of rat liver S9. These results suggest that there was a possibility of metabolic activation due to nitroreductase being present in CHL cells, as well as Salmonella mutagenicity (Sera et al., 1992
), but not in rat liver microsomes.
As for the chemical properties of the four derivatives, two reversible waves involving a one-electron transfer process were observed (Fukhara et al., 1992). The first half-wave redox potential of nitrated 6-ABPs, such as 1or 3-N-6-ABP, was higher than that of mononitroB[a]Ps, such as 1or 3-nitroB[a]P, and, in addition, that of their N-oxides was also higher: 1- and 3-N-6-ABPO were reduced to anion radicals much more easily than mononitroB[a]P (Fukhara et al., 1992). As indicated previously, the mutagenicity of 3-N-6-ABP and 3-N-6-ABPO for Salmonella strains TA98 and YG1024, an acetyltransferase-rich mutant of TA98, showed 348 and 7670, and 1260 and 30 500 revertants/ng without the S9 mix, respectively. The 3-N-6-ABP was more mutagenic than 1-N-6-ABP (352 and 2750 revertants/ng, respectively), and 3-N-6-ABPO was more mutagenic than 1-N-6-ABPO (115 and 1930 revertants/ng, respectively). It has also been found that the mutagenicity and tumorigenicity of 3,6-dinitroB[a]P were more potent than those of 1,6-dinitroB[a]P (Horikawa et al., 1998
; Sera et al., 1991
): the difference in the activity may cause metabolic pathways dependent on nitro reduction (Sera et al., 1992
). There was also an association between biological activity and the electrochemical reduction of related compounds.
On the other hand, nitro-azaB[a]P was detected from semivolatile materials passed through a 0.45 µm filter on airborne and diesel particulate matter (Sera et al., 1994
). It is likely that related compounds may be present as a coating chemical on elemental carbon or as a semivolatile form involved with smaller particles inhaled into lung alveoli, and were deposited in lung tissues (Tokiwa et al., 1993
, 1998
). Normally, most organic chemicals are identified by gas-chromatography and mass spectrometry, but these compounds could be directly determined by mass spectrometric analysis after purification using liquid column chromatography. The compounds were detected on the column at an oven temperature programmed from 80 to 310°C (Sera et al., 1994
). Under these conditions, 1- and 3-N-6-ABP or ABPO were detected at the levels from 0.8 to 7.7 ng/g of material. In our earlier study on the ABPs and ABPOs, the production of 8-hydroxyguanosine as a result of oxidative damage in cellular DNA, resulted in a marked increase compared with other related nitroarenes, although this was in vivo data from formed mouse lungs (unpublished data). These results suggest that these ABPs and ABPOs generated oxygen free radicals (or hydroxyl radicals) in the mouse lung, and led to mutation at the deoxyguanosine residue in the DNA. These results indicate that the ABPs and ABPOs induced not only bacterial mutation and genotoxic action in vitro, but also pulmonary injury as a result of oxidative damage.
The sources and formation of these chemicals in the environment have not been chemically-revealed in the present study. However, these are serious mutagens that elevate cardiopulmonary and lung cancer incidence.
| Notes |
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3 To whom correspondence should be addressed. Tel: +81 93 693 3088; Email: tokiwa{at}kwuc.ac.jp
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Received on October 16, 2000; accepted on October 20, 2000.
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