Cytogenetic effects of cigarette smoke on pulmonary alveolar macrophages of the rat

Cigarette smoke inhalation aggravates diabetic kidney injury in rats

Diabetic kidney disease (DKD) is the leading cause of end-stage kidney disease. Epidemiological studies have demonstrated that cigarette smoke or nicotine is a risk factor for the progression of chronic kidney injury. The present study analyzed the kidney toxicity of cigarette smoke in experimental rats with DKD. Experimental diabetes was induced in 7-week-old Sprague-Dawley rats by a single intraperitoneal injection of streptozotocin (60 mg kg^-1). Four weeks after the induction of diabetes, rats were exposed to cigarette smoke (200 μg L^-1), 4 h daily, and 5 days per week for 4 weeks. Cigarette smoke did not affect the levels of plasma glucose, hemoglobin A1c, high-density lipoprotein cholesterol, low-density lipoprotein cholesterol or non-esterified fatty acids in both control and diabetic rats under the experimental conditions. Cigarette smoke, however, significantly increased diabetes-induced glomerular hypertrophy and urinary kidney injury molecule-1 (KIM-1) and neutrophil gelatinase-associated lipocalin (NGAL) excretion, suggesting exacerbation of diabetic kidney injury. Cigarette smoke promoted macrophage infiltration and fibrosis in the diabetic kidney. As expected, cigarette smoke increased oxidative stress in both control and diabetic rats. These data demonstrated that four weeks of exposure to cigarette smoke aggravated the progression of DKD in rats.

Dose-related cytogenetic damage in pulmonary alveolar macrophages from mice exposed to cigarette smoke early in life

The micronucleus test detects both structural and numerical chromosomal aberrations caused by environmental agents. However, this test is poorly sensitive to detect the clastogenicity of cigarette smoke (CS) in human peripheral blood lymphocytes. At variance with peripheral blood lymphocytes and other cells outside the lower respiratory tract, pulmonary alveolar macrophages (PAM) are selectively affected by inhalable carcinogens and have been used to evaluate the modulation of CS-related cytogenetic alterations in vivo. The present study was aimed at evaluating (1) the cytogenetic response in PAM isolated from the lung of mice exposed to CS during the first 4 weeks of life and (2) the dose dependence of MN and polynucleated (PN) PAM formation in CS-exposed mice. To this purpose, ICR(CD-1) mice were exposed whole body to mainstream CS for 4 weeks, starting immediately after birth. Bronchoalveolar lavage (BAL) was performed to evaluate the cellularity of this fluid and the frequency of PN and MN PAM. At the doses of 119, 292, and 438 mg/m(3) total particulate matter, CS significantly increased both the proportion of PAM in the BAL fluid and the frequencies of PN and MN PAM. The cytogenetic effects were significantly correlated with the CS dose. In conclusion, PAM are suitable to detect induction by CS of clastogenic and aneugenic effects in mice during a developmental period corresponding to infancy, childhood, and early adolescence in humans. These surrogate cells, providing an important defense mechanism of the respiratory tract, are proposed as indicators of CS-related DNA damage in youngsters.

Genotoxicity of environmental tobacco smoke: a review

Environmental tobacco smoke (ETS), or second-hand smoke, is a widespread contaminant of indoor air in environments where smoking is not prohibited. It is a significant source of exposure to a large number of substances known to be hazardous to human health. Numerous expert panels have concluded that there is sufficient evidence to classify involuntary smoking (or passive smoking) as carcinogenic to humans. According to the recent evaluation by the International Agency for Research on Cancer, involuntary smoking causes lung cancer in never-smokers with an excess risk in the order of 20% for women and 30% for men. The present paper reviews studies on genotoxicity and related endpoints carried out on ETS since the mid-1980s. The evidence from in vitro studies demonstrates induction of DNA strand breaks, formation of DNA adducts, mutagenicity in bacterial assays and cytogenetic effects. In vivo experiments in rodents have shown that exposure to tobacco smoke, whole-body exposure to mainstream smoke (MS), sidestream smoke (SS), or their mixture, causes DNA single strand breaks, aromatic adducts and oxidative damage to DNA, chromosome aberrations and micronuclei. Genotoxicity of transplacental exposure to ETS has also been reported. Review of human biomarker studies conducted among non-smokers with involuntary exposure to tobacco smoke indicates presence of DNA adducts, urinary metabolites of carcinogens, urinary mutagenicity, SCEs and hypoxanthine-guanine phosphoribosyltransferase (HPRT) gene mutations (in newborns exposed through involuntary smoking of the mother). Studies on human lung cancer from smokers and never-smokers involuntarily exposed to tobacco smoke suggest occurrence of similar kinds of genetic alterations in both groups. In conclusion, these overwhelming data are compatible with the current knowledge on the mechanisms of carcinogenesis of tobacco-related cancers, occurring not only in smokers but with a high biological plausibility also in involuntary smokers.

Genotoxicity of tobacco smoke and tobacco smoke condensate: a review

This report reviews the literature on the genotoxicity of mainstream tobacco smoke and cigarette smoke condensate (CSC) published since 1985. CSC is genotoxic in nearly all systems in which it has been tested, with the base/neutral fractions being the most mutagenic. In rodents, cigarette smoke induces sister chromatid exchanges (SCEs) and micronuclei in bone marrow and lung cells. In humans, newborns of smoking mothers have elevated frequencies of HPRT mutants, translocations, and DNA strand breaks. Sperm of smokers have elevated frequencies of aneuploidy, DNA adducts, strand breaks, and oxidative damage. Smoking also produces mutagenic cervical mucus, micronuclei in cervical epithelial cells, and genotoxic amniotic fluid. These data suggest that tobacco smoke may be a human germ-cell mutagen. Tobacco smoke produces mutagenic urine, and it is a human somatic-cell mutagen, producing HPRT mutations, SCEs, microsatellite instability, and DNA damage in a variety of tissues. Of the 11 organ sites at which smoking causes cancer in humans, smoking-associated genotoxic effects have been found in all eight that have been examined thus far: oral/nasal, esophagus, pharynx/larynx, lung, pancreas, myeoloid organs, bladder/ureter, uterine cervix. Lung tumors of smokers contain a high frequency and unique spectrum of TP53 and KRAS mutations, reflective of the PAH (and possibly other) compounds in the smoke. Further studies are needed to clarify the modulation of the genotoxicity of tobacco smoke by various genetic polymorphisms. These data support a model of tobacco smoke carcinogenesis in which the components of tobacco smoke induce mutations that accumulate in a field of tissue that, through selection, drive the carcinogenic process. Most of the data reviewed here are from studies of human smokers. Thus, their relevance to humans cannot be denied, and their explanatory powers not easily dismissed. Tobacco smoke is now the most extreme example of a systemic human mutagen.

Cigarette smoke induces anaphase bridges and genomic imbalances in normal cells

Exposure to cigarette smoke has long been linked to carcinogenesis, but the emphasis has been placed on mutational changes in the DNA sequence caused by the carcinogens in smoke. Here, we report an additional role for cigarette smoke exposure in contributing to chromosomal aberrations in cells. We have found that cigarette smoke condensate (CSC) induces anaphase bridges in cultured human cells, which in a short time lead to genomic imbalances. The frequency of the induced bridges within the entire population decreases with time, and this decrease is not dependent upon the p53-mediated apoptotic pathway. Additionally, we show that CSC induces DNA double stranded breaks (DSBs) in cultured cells and purified DNA. The reactive oxygen species (ROS) scavenger, 2' deoxyguanosine 5'-monophosphate (dGMP) prevents CSC-induced DSBs, anaphase bridge formation and genomic imbalances. Therefore, we propose that CSC induces bridges and genomic imbalances via DNA DSBs. Furthermore, since the amount of CSC added to the cultures was substantially less than that extracted from a single cigarette, our results show that even low levels of cigarette smoke can cause irreversible changes in the chromosomal constitution of cultured cells.

Less than additive interaction between cigarette smoke and chromium(VI) in inducing clastogenic damage in rodents

A combination of tobacco smoking with certain agents has been shown to exert synergistic carcinogenic effects. On the other hand, antagonism betweeen smoke and other pulmonary carcinogens has also been documented by both epidemiological and experimental data. In spite of a very large number of studies carried out for decades in workers exposed to hexavalent chromium, the influence of smoking habits on lung carcinogenesis induced by this metal has not been clarified. For this reason, we performed two studies evaluating clastogenic effects in rodents. In the first one, BDF(1) mice were exposed whole-body to mainstream cigarette smoke for 5 days and, on the last day, they received an i.p. injection of potassium dichromate. In the second study, Sprague-Dawley rats were exposed whole-body to environmental cigarette smoke for 18 consecutive days and for the same period of time they received daily intra-tracheal instillations of sodium dichromate. Individually, the two hexavalent chromium salts and cigarette smoke, either mainstream or environmental, enhanced the frequency of micronuclei in bone marrow polychromatic erythrocytes of both mice and rats. Moreover, individual exposure to either environmental cigarette smoke or sodium dichromate enhanced the frequency of micronuclei and multiple nuclei in pulmonary alveolar macrophages of rats. In both studies, combined exposure to cigarette smoke and hexavalent chromium produced less than additive clastogenic effects. These results are consistent with our previous data, showing that hexavalent chromium and either benzo[a]pyrene or cigarette smoke condensate behave antagonistically in in vitro mutagenicity test systems and that the chromium reducing capacity of human pulmonary alveolar macrophages and peripheral lung parenchyma is enhanced in smokers. Taken together, in the absence of any epidemiological evidence, these findings rule out any occurrence of synergism between cigarette smoke and hexavalent chromium, at least in certain stages of the carcinogenesis process.

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.

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.

Molecular toxicology endpoints in rodent inhalation studies

Although histopathology will continue to be essential for assessing the results of rodent inhalation studies, molecular toxicology endpoints are of increasing importance, as these techniques often complement and extend histopathological examinations. One of the primary uses of molecular toxicology is determining the delivered dose of the inhaled material to macromolecules in target tissues. During inhalation studies this is most often done by measuring DNA adducts in the respiratory tract. DNA adducts may be measured specifically (e.g. using monoclonal antibodies or mass spectrometry) or non-specifically (e.g. by using the 32P-post-labeling assay). Another major use of molecular toxicology techniques is the assessment of cellular and molecular changes in target tissues which may precede or be more sensitive than histopathologic alterations. For example, rates of cellular DNA synthesis occurring in target tissues may be quantified at any time during the study by administering the animals either radiolabelled thymidine or the non-radiolabelled thymidine analog bromodeoxyuridine (BrdU). Pulmonary changes may be assessed in bronchoalveolar lavage fluid using either cellular (e.g. macrophage number, granulocyte number) or biochemical (e.g. alkaline phosphatase, lactate dehydrogenase) techniques. The potential of the inhaled material to produce genetic alterations may be evaluated by examining the chromosomes of pulmonary alveolar macrophages for cytogenetic changes. To illustrate the use of these endpoints, an experiment was conducted to determine the molecular toxicology of aged and diluted sidestream smoke (a surrogate for environmental tobacco smoke) in rodent inhalation studies. The endpoints measured were DNA adducts in target and non-target tissue, chromosome aberrations in pulmonary alveolar macrophages, and DNA synthesis in the epithelial lining of the nasal turbinates.

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.

Coclastogenicity of ethanol with cigarette smoke in rat erythroblasts and anticlastogenicity in alveolar macrophages

A series of experiments was carried out to assess cytotoxic and cytogenetic effects in bone marrow polychromatic erythrocytes (PCE) and pulmonary alveolar macrophages (PAM) resulting from individual or combined exposure of male BD6 rats to ethanol, cigarette smoke and Aroclor 1254. Addition of 5% ethanol to drinking water did not affect the micronucleus frequency but consistently enhanced the proportion of polynucleated PAM. Moreover, the higher concentration used (10%) was cytotoxic in the bone marrow. Whole-body exposure to cigarette smoke elevated the micronucleus frequency in both PCE (4.0-4.4-fold) and PAM (2.0-3.6-fold) and enhanced the frequency of polynucleated PAM. After 3 weeks of combined exposure, ethanol produced contrasting effects in smoke-exposed rats, i.e. an increase of micronuclei in PCE and a decrease in PAM. An i.p. injection of Aroclor 1254 was per se devoid of any influence on the monitored parameters but tended to attenuate the cytotoxic and cytogenetic changes produced by cigarette smoke or ethanol in both types of cell.

Inhalation exposure of rats to metal aerosol. II. Study of mutagenic effect on alveolar macrophages

The effects of inhalation exposure to metal aerosol derived from nickel refinery waste were studied on the frequency of chromosome aberrations in alveolar macrophages in Wistar rats. A 4-month exposure period resulted in significant (P less than 0.01) increases in chromosome aberrations. Relatively high variability without statistical significance was observed after a 4-week exposure period. Increase in damaged alveolar macrophages with the length of exposure seems to point to the role of pulmonary metal deposits. Comparison of the results with those found after 6 months of exposure in bone marrow cells confirmed that metal particles in nickel refinery waste are genotoxic. Thus, this study indicates that alveolar macrophages are suitable for monitoring the genotoxic potential of hazardous chemicals administered by inhalation.

Chromosome damage in rat pulmonary alveolar macrophages following ozone inhalation

To determine whether ozone is clastogenic at environmentally relevant exposure levels, rats were exposed for 6 h to 0.0, 0.12, 0.27, or 0.80 ppm ozone. The alveolar macrophages were isolated from animals sacrificed 28 h after the end of the exposure. The mitotic index and frequency of chromosome aberrations were determined. No change in the mitotic index was detected following 0.12 ppm ozone exposure. A significant decrease in mitotic index was observed after exposure to 0.27 ppm ozone; a significant (4-fold) increase in the frequency of dividing macrophages was detected following exposure to 0.8 ppm ozone. Only chromatid-type aberrations were observed. There was a significant increase in the frequency of cells with chromatid gaps and in the frequency of cells with chromatid deletions. Animals exposed to 0.27 ppm ozone had the highest proportion of cells with chromatid deletions (0.172) relative to background level (0.028). No exchanges or chromosome-type aberrations were detected in any of the animals. These data suggest that ozone, at relatively low levels, is clastogenic in macrophages from exposed rats.