Chromosome damage in rat pulmonary alveolar macrophages following ozone inhalation

Detection of poly(ADP-ribose) synthetase activity in alveolar macrophages of rats exposed to nitrogen dioxide and ozone

The toxic effects of nitrogen dioxide (NO2) and ozone (O3) are mediated through the formation of free radicals, which can cause DNA strand breaks. The present study demonstrates that exposure to NO2 and O3 causes a stimulation of poly(ADP-ribose) (polyADPR) synthetase in alveolar macrophages of rats. Three-month-old male Sprague-Dawley rats, specific pathogen free, were exposed to either 1.2 ppm NO2 or 0.3 ppm O3 alone or a combination of these 2 oxidants continuously for 3 days. The control group was exposed to filtered room air. To evaluate whether exposure to these two oxidants (NO2 and O3) caused DNA damage to lung cells, the activity of polyADPR synthetase was measured. Cellular DNA repair is dependent upon the formation of poly(ADP-ribose) polymerase, which is catalyzed by polyADPR synthetase. PolyADPR synthetase is known to be activated in response of DNA damage. The results showed that the enzyme activity was stimulated after exposure to O3 or exposure to NO2 + O3. Ozone exposure caused a 25% increase in the enzyme activity as compared to the control. Combined exposure to NO2 + O3 showed a 53% increase in the enzyme activity. These results were statistically significant as compared to the control and NO(2) exposure groups. Other parameters such as total cell count, cell viability, and differential cell count were also determined. The stimulation of polyADPR synthetase activity after O3 exposure or NO2 + O3 exposure reflects a response to lung cellular DNA repair, which may be used as an indicator for assessing DNA damage caused by oxidant injury.

DNA strand breaks caused by exposure to ozone and nitrogen dioxide

The present study demonstrates that exposure to ozone (O3) and nitrogen dioxide (NO2) can cause DNA single-strand breaks in alveolar macrophages. Three-month-old male Sprague-Dawley rats, specific pathogen free, were exposed to either 1.2 ppm NO2 or 0.3 ppm O3 alone or a combination of these two oxidants continuously for 3 days. The control group was exposed to filtered room air. The oxidant effects were substantiated by determining total and differential cell counts, lactate dehydrogenase activity, and total soluble protein in bronchoalveolar lavage. DNA damage was measured as single-strand breaks by alkaline elution assay. The results showed that, relative to control, NO2 exposure did not cause any significant change in the parameters studied. Exposure to O3 and combined exposure to NO2 and O3 caused significant changes in all parameters studied except cell viability. The rates of elution (Kc) of single-strand DNA from polycarbonate filter for O3 exposure and combined exposure were 73 and 79% faster than that of the control, respectively. The amounts of DNA single-strand breaks caused by O3 and combined exposure were significantly greater than the amounts detected for the NO2-exposed and control groups.

Genotoxic changes in the pulmonary alveolar macrophages of mice, rats and hamsters treated with tobacco smoke

To determine whether tobacco smoke (TS) is genotoxic for lung tissue macrophages (pulmonary alveolar macrophages, PAM) as a general result of its inhalatory action BD6 rats, Syrian golden hamsters and BDF1 (C57BlxDBA2) mice were subjected to wholebody exposure for 90 or 60 min daily (600 cm3 mainstream smoke in 16-1 glass chamber, 9 or 6 exposures of 15 min each, respectively), for different periods ranging up to 30 days. A significant enhancement of the frequency of polynucleated macrophages (BiN PAM) was observed in all animal species after more than 10-days of repeated exposure to TS. The increased level of BiN PAM (the number of bi- (+) poly-nucleated PAM) correlates with the duration of exposure to TS: on day 20 after the start of inhalation, more than 25/1000 of mice PAM were polynucleated, while on day 30 this applied to approximately 50/1000. Furthermore, a highly significant increase in the level of micronucleated PAM (MN PAM) was also established after 10 days TS treatment of mice and persisted to the end of these examinations. TS was effective in enhancing the micronucleated and polynucleated PAM levels in hamsters irrespective of their sex, as it was in male BD6 rats aged 2 or 11 months. It appears that TS induces a more pronounced elevation of polynucleated PAM frequency in rats than in hamsters and mice. These data suggest that inhaled TS is genotoxic in alveolar macrophages in all exposed species of laboratory animals. An attempt was made to trace the possible clastogenic effect of a single i.p. administration of cyclophosphamide (CP, 15 mg/kg) in mice simultaneously in bone marrow and in PAM. A definite clastogenic effect in bone marrow 24 h and 48 h after CP injection and a total absence of changes in PAM from the lungs during the 15-day period after clastogen exposure were established. These data may support the hypothesis of local production of PAM in the lung from their proliferative precursor. The results provide evidence that PAM in laboratory animals are a sensitive and useful target for assessing harmful effects associated with environmental chemical factors that can be inhaled, including TS.

Products of ozonized arachidonic acid potentiate the formation of DNA single strand breaks in cultured human lung cells

In this study we examined the potential for environmental levels of ozone (03) to degrade arachidonic acid (AA), a polyunsaturated fatty acid abundantly present in the lung, into products that can produce DNA single strand breaks (ssb) in cultured human lung cells. Human lung fibroblasts were incubated with 60 microM AA that had been previously exposed to and degraded by 0.4 ppm 03 (1 hr.) Incubation of the cells with 03-exposed AA (but not with vehicle alone) for 1 hr at 4 degrees C and 37 degrees C produced 555 and 245 rad-equivalents of DNA ssb, respectively, as determined by the DNA alkaline elution technique. These breaks were completely eliminated when the ozonized AA solution was incubated with catalase prior to cell treatment, indicating that h202 was solely responsible for damaging DNA. Superoxide dismutase bovine serum albumin, or heat-inactivated catalase showed little, if any, inhibitory activity. The H202 content of the ozonized AA (31 +/- 4 microM) could account for only about 40% of the observed breaks. Potentiation of the H202-induced DNA ssb persisted after removal of the carbonyl substances by chromatographic procedures, suggesting that the non-carbonyl component of ozonized AA was the responsible component for inducing augmentation of the observed increases in DNA ssb. Ozonized AA also induced DNA ssb in cultures of the human bronchial epithelial cell line BEAS-2B. Again, these breaks were shown to exceed levels that could be attributed to the presence of H202 alone. These results indicate that products of ozonized AA can interact to potentiate DNA ssb in human lung cells.

Micronucleus assay in pulmonary alveolar macrophages, a simple model to detect genotoxicity of environmental agents entering through the inhalation route

A simple and short-term micronucleus (MN) test in pulmonary alveolar macrophages (PAMs) of rats has been developed to assess potential genotoxic effects of gaseous environmental agents. The protocol has been tested in model experiments with indoor air pollutants like mosquito coil smoke (MCS) and mosquito mat vapour (MMV). Smears of pulmonary lavage fluid collected in hypotonic (0.56%) KCl solution were fixed in absolute methanol and stained in Giemsa (10%). Characteristically the large size of the PAMs facilitates easy scoring of MN. An interval of 32 h post exposure seems to be suitable for MN preparation. A comparison of the concentration-response data on CAs (at 24 h post exposure) and MN (at 32 h post exposure) clearly reveals the validity of the MN assay in PAMs.

Induction of chromosome aberrations and micronuclei in pulmonary alveolar macrophages of rats following inhalation of mosquito coil smoke

The genotoxic potential of inhalation of mosquito coil (MC) smoke was evaluated by using metaphase chromosome aberration and micronucleus assays in pulmonary alveolar macrophages (PAMs) of rats following short-term as well as long-term whole body intermittent exposure. For short-term exposure, the animals were exposed for 15 min/h, 8 h/day to smoke collected for 1, 5 or 10 min, and they were killed 16 or 24 h after the final exposure. For long-term exposure, they were exposed for 15 min/h, 8 h/day, 7 days/week to smoke collected for 10 min and then they were killed 24 h after the final exposure. Each time before exposure, fresh smoke was collected by burning a mosquito coil. Pulmonary lavage was collected, and conventional flame-drying preparation was done for metaphase chromosome analysis and micronuclei (MN) were analyzed from smear preparations. Significantly higher frequencies of chromosome aberrations, including as well as excluding gaps, and micronucleated PAMs in smoke-exposed animals, compared to controls, indicated genotoxic capacity of MC smoke. The increases significantly correlated with the "concentration" of the gas. Mitotic indices also showed a significant and concentration-dependent increase. The frequencies of chromosome aberrations and MN following 7-day exposure were very similar to those for 1-day exposure. This was probably due to the transient nature of PAMs. A post-exposure gap of 24 h, compared to the 16-h gap, yielded a higher incidence of both mitoses and chromosome aberrations.

Review of the genotoxicity of ozone

Ozone is a powerful oxidant, reactive to biomolecules. In aqueous solution it decomposes to give hydrogen peroxide, superoxide and hydroxy radicals which can take part in secondary reactions. Ozone is a disinfectant that inactivates both viruses and bacteria. Although other reactions are primarily responsible for the inactivation, cellular DNA is also damaged. Ozone is genotoxic to microorganisms, plants and cell cultures in vitro. The results from in vivo cytogenetic studies with laboratory animals after inhalation exposure are contradictory. Chromosome aberrations in lymphocytes, but not SCEs, have been demonstrated in Chinese hamsters but not in mice. Chromatid deletions were induced in pulmonary macrophages in rats. No cytogenetic effects have been reported for bone marrow cells or spermatocytes. The few experimental and epidemiological studies with human subjects do not allow a conclusion on the cytogenetic effects of ozone in lymphocytes in humans. No life-long cancer studies have been performed with ozone. However, after 4 and 6 months of inhalation exposure, lung adenomas were induced in strain A/J mice, but not in Swiss-Webster mice.