Effect of vitamin levels on biomarkers of exposure and oxidative damage-the EXPAH study.

DNA adducts are markers of carcinogen exposure and of their biological effect; they have been shown to be related to mutagenesis, and therefore they could be a predictive biomarker of human cancer. The objective of this study was to assess if there is a relationship between vitamins A, C, and E, which are known to play a significant role as free radical scavengers and antioxidant agents, and biomarkers of genotoxicity and oxidative stress. Three hundred and fifty-six subjects from Czech Republic, Slovak Republic and Bulgaria, who completed a questionnaire on dietary information and had a measurement of plasma A, C, E vitamins, DNA adduct levels (benzo[a]pyrene (B[a]P) and bulky (DNA-Tot) DNA adducts) and oxidative damage (cyclic pyrimidopurinone N-1,N2 malondialdehyde-2 deoxyguanosine (M1dG) and 8-oxo-7,8-dihydro-2_deoxyguanosine (8-oxodG)) were analyzed. A significant inverse correlation was observed between plasma vitamin levels and both benzo[a]pyrene (B[a]P) and bulky DNA adducts. Vitamin A was also significantly inversely correlated with M1dG, a marker of oxidative damage. The associations were stronger in non-smokers than in smokers. Dietary intake of certain antioxidants such as vitamins is associated with reduced levels of markers of DNA damage (B[a]P and DNA-Tot) and oxidation (M1dG and 8-oxodG) measured in peripheral white blood cells. This could contribute to the protective role of such a dietary pattern on cancer risk. The protective effect of dietary vitamins is less evident in smokers.

Temporal variation in the genotoxic potential of urban air particulate matter.

The main aim of this study was to compare the genotoxic potential of organic extracts from urban air particles collected in three different sampling periods in the center of Prague (Czech Republic). For this purpose, we analyzed the DNA adduct forming activity of extractable organic matter (EOM) from urban air particles <10 microm (PM10) in the human hepatoma cell line HepG2. DNA adducts were analyzed by (32)P-postlabelling with nuclease P1 enrichment. PM10 concentrations were 36.9 microg/m(3), 62.6mug/m(3) and 39.0 microg/m(3), in summer 2000, winter 2001 and winter 2005, respectively. The corresponding EOM contents were 5.0 microg/m(3) (13.9% of PM10), 14.9 microg/m(3) (23.8%) and 6.7 microg/m(3) (17.2%). The total DNA adduct levels induced by 10 microg EOM/ml were 4.7, 19.5 and 37.2 adducts/10(8) nucleotides in summer 2000, winter 2001 and winter 2005, respectively. However, when the EOM quantities per cubic meter of air were taken into consideration, the summer sample exhibited a 10-fold lower genotoxicity than did those of winter, while the difference between the winter samples was not significant: 23.4 in summer 2000, 291 in winter 2001 and 249 in winter 2005 (in relative units). Although the PM10 concentration in air and the EOM content in particles in winter 2005 were significantly lower than in winter 2001, the genotoxic potential of the ambient air in these samples was almost equal. There were significant positive correlations between the B[a]P and c-PAH content in EOM from various sampling periods and the total DNA adduct levels detected in the EOM-treated samples. These findings support the hypothesis that the B[a]P and c-PAH content in EOM is the most important factor that determines its genotoxic potential. Thus, estimating the genotoxic potential of the ambient air and predicting health risk should be based mainly on the c-PAH concentration and the biological activity of the extracts, while the mass of particles and the EOM content do not seem to be crucial determinants of ambient air genotoxicity.

In vitro genotoxicity of PAH mixtures and organic extract from urban air particles part II: human cell lines.

Principal aims of this study were at first, to find a relevant human derived cell line to investigate the genotoxic potential of PAH-containing complex mixtures and second, to use this cell system for the analysis of DNA adduct forming activity of organic compounds bound onto PM10 particles. Particles were collected by high volume air samplers during summer and winter periods in three European cities (Prague, Kosice, and Sofia), representing different levels of air pollution. The genotoxic potential of extractable organic matter (EOM) was compared with the genotoxic potential of individual carcinogenic polycyclic aromatic hydrocarbons (c-PAHs) as well as their artificial mixtures. Metabolically competent human hepatoma HepG2 cells, confluent cultures of human diploid lung fibroblasts (HEL), and the human monocytic leukemia cell line THP-1 were used as models. DNA adducts were analyzed by (32)P-postlabeling. The total DNA adduct levels induced in HepG2 cells after exposure to EOMs were higher than in HEL cells treated under the same conditions (15-190 versus 2-15adducts/10(8) nucleotides, in HepG2 and HEL cells, respectively). THP-1 cells exhibited the lowest DNA adduct forming activity induced by EOMs (1.5-3.7adducts/10(8) nucleotides). A direct correlation between total DNA adduct levels and c-PAH content in EOM was found for all EOMs in HepG2 cells incubated with 50microg EOM/ml (R=0.88; p=0.0192). This correlation was even slightly stronger when B[a]P content in EOMs and B[a]P-like adduct spots were analyzed (R=0.90; p=0.016). As THP-1 cells possess a limited metabolic capacity for most c-PAHs to form DNA reactive intermediates and are also more susceptible to toxic effects of PAHs and various EOM components, this cell line seemed to be an inappropriate system for genotoxicity studies of PAH-containing complex mixtures. The seasonal variability of genotoxic potential of extracts was stronger than variability among the three localities studied. In HepG2 cells, the highest DNA adduct levels were induced by EOM collected in Prague in the winter period, followed by Sofia and Kosice. However, in the summer sampling period, the order was quite opposite: Kosice>Sofia>Prague. When the EOM content per m(3) of air was taken into consideration in order to compare real exposures of humans to genotoxic compounds in all three localities, extracts from respirable dust particles collected in Sofia exhibited the highest genotoxicity regardless of the sampling period. The results indicate that most of DNA adducts detected in cells incubated with EOMs have their origin in low concentrations of c-PAHs representing 0.03-0.17% of EOM total mass. Finally, our results suggest that HepG2 cells have a metabolic capacity for PAHs similar to human hepatocytes and represent therefore the best in vitro model for investigating the genotoxic potential of complex mixtures containing PAHs among the three cell lines tested in this study.

Biomarkers of air pollution exposure--a study of policemen in Prague.

The effect of exposure to organic compounds adsorbed onto respirable air particles (<2.5microm) on DNA adducts in lymphocytes was studied in a group of non-smoking policemen (N=109, aged 35+/-0.9 years) working in the downtown area of Prague and spending >8h daily outdoors. Personal exposure to carcinogenic polycyclic aromatic hydrocarbons (c-PAHs) adsorbed on respirable particles was monitored in each subject for 48h before biological sampling. DNA adducts were analyzed by a (32)P-postlabelling assay, and total DNA adduct levels and B[a]P-like spots were determined. Further biomarkers included cotinine levels in urine to control for exposure to tobacco smoke, plasma levels of vitamins A, E and C and polymorphisms of metabolic genotypes (GSTM1, GSTP1, GSTT1, CYP 1A1-Msp I and Ile/Val, MTHFR, MS), DNA repair genotypes (XRCC1, hOGG1 and XPD exons 6 and 23) and the p53 gene (p53 Msp I and BstU I). All the biomarkers of exposure and effect were analyzed repeatedly during a period of one year at 2-3 month intervals (January, March, June, September 2004) to cover periods with high (winter) and low (summer) levels of air pollution. The highest personal exposure to c-PAHs was found in January (8.1+/-8.8ng/m(3)), while the other three sampling periods exhibited 3-4-fold lower c-PAH exposure. The total DNA adducts were only slightly elevated in January (2.08+/-1.60) compared to March (1.66+/-0.65), June (1.96+/-1.73) and September (1.77+/-1.77). B[a]P-like DNA adducts, however, were significantly higher in January than in the March and June sampling periods (0.26+/-0.14 vs. 0.19+/-0.12 and 0.22+/-0.13, respectively; p<0.0001 and p=0.017) indicating that c-PAH exposure probably plays a crucial role in DNA adduct formation in lymphocytes. No effect of individual metabololic or DNA repair genotypes on DNA adduct levels was observed. However, the combination of two genotypes encoding enzymes metabolizing c-PAHs - CYP 1A1 and GSTM1 - was associated with the levels of total and B[a]P-like DNA adducts under conditions of increased exposure to c-PAHs. Our study suggests that DNA adducts in the lymphocytes of subjects exposed to increased c-PAH levels are an appropriate biomarker of a biologically effective dose, directly indicating whether or not the extent of exposure to these compounds is related to an increased mutagenic and carcinogenic risk.

In vitro genotoxicity of PAH mixtures and organic extract from urban air particles part I: acellular assay.

Acellular assay of calf thymus DNA+/-rat liver microsomal S9 fraction coupled with (32)P-postlabelling was used to study the genotoxic potential of organic compounds bound onto PM10 particles collected in three European cities-Prague (CZ), Kosice (SK) and Sofia (BG) during summer and winter periods. B[a]P alone induced DNA adduct levels ranging from 4.8 to 768 adducts/10(8) nucleotides in the concentration dependent manner. However, a mixture of 8 c-PAHs with equimolar doses of B[a]P induced 3.7-757 adducts/10(8) nucleotides, thus suggesting the inhibition of DNA adduct forming activity by interaction among various PAHs. Comparison of DNA adduct levels induced by various EOMs indicates higher variability among seasons than among localities. DNA adduct levels for Prague collection site varied from 19 to 166 adducts/10(8) nucleotides, for Kosice from 22 to 85 and for Sofia from 6 to 144 adducts/10(8) nucleotides. Bioactivation with S9 microsomal fraction caused 2- to 7-fold increase in DNA adduct levels compared to -S9 samples, suggesting a crucial role of indirectly acting genotoxic EOM components, such as PAHs. We have demonstrated for the first time a significant positive correlation between B[a]P content in EOMs and total DNA adduct levels detected in the EOM treated samples (R=0.83; p=0.04). These results suggest that B[a]P content in EOM is an important factor for the total genotoxic potential of EOM and/or B[a]P is a good indicator of the presence of other genotoxic compounds causing DNA adducts. Even stronger correlation between the content of genotoxic compounds in EOMs and total DNA adduct levels detected (R=0.94; p=0.005) was found when eight c-PAHs were taken into the consideration. Our findings support a hypothesis that a relatively limited number of EOM components is responsible for a major part of its genotoxicity detectable as DNA adducts by (32)P-postlabelling.

[Parental smoking and exposure of pre-school children to tobacco smoke]. / Kourení rodicu a expozice predskolních detí tabákovému kouri.

BACKGROUND: During studies on the health of children aged 3 or 4.5 years in Teplice and Prachatice districts of the Czech Republic, we focused also on the extent of smoking in the families and exposure of children to environmental tobacco smoke. METHODS AND RESULTS: In 1128 questionnaires administered to mothers of children born in 1994-1998, 35.6% of mothers indicated that they smoked and 48.9% of fathers/partners (N = 1075) were smokers. Including other family members, there were 41.6% families without any smoker, 30.1% of families with one smoker and 24% families with two smokers (out of 1061 households). Urine samples of 523 pairs of mothers and children (aged 4.5 years) were assayed for cotinine using a RIA radioimmunoassay. Concentration of cotinine was higher than 500 ng cotinine/mg creatinine (the cut-off value for smoking) in 199 of 523 mothers (38%). Exposure of children to environmental tobacco smoke (cotinine levels over 20ng/mg creatinine) was detected in 48.2% of 523 children. There were more children with cotinine levels over 20 ng in Teplice (59.2% of 287 children) than in Prachatice district (34.7% of 236 children). CONCLUSIONS: Cotinine levels in child's urine were significantly positively associated with maternal cotinine levels as well as with smoking of mother and father, and were lower in children visiting kindergarten.

Molecular epidemiology studies on occupational and environmental exposure to mutagens and carcinogens, 1997-1999.

Molecular epidemiology is a new and evolving area of research, combining laboratory measurement of internal dose, biologically effective dose, biologic effects, and influence of individual susceptibility with epidemiologic methodologies. Biomarkers evaluated were selected according to basic scheme: biomarkers of exposure--metabolites in urine, DNA adducts, protein adducts, and Comet assay parameters; biomarkers of effect--chromosomal aberrations, sister chromatid exchanges, micronuclei, mutations in the hypoxanthine-guanine phosphoribosyltransferase gene, and the activation of oncogenes coding for p53 or p21 proteins as measured on protein levels; biomarkers of susceptibility--genetic polymorphisms of genes CYP1A1, GSTM1, GSTT1, NAT2. DNA adducts measured by 32P-postlabeling are the biomarker of choice for the evaluation of exposure to polycyclic aromatic hydrocarbons. Protein adducts are useful as a biomarker for exposure to tobacco smoke (4-aminobiphenyl) or to smaller molecules such as acrylonitrile or 1,3-butadiene. Of the biomarkers of effect, the most common are cytogenetic end points. Epidemiologic studies support the use of chromosomal breakage as a relevant biomarker of cancer risk. The use of the Comet assay and methods analyzing oxidative DNA damage needs reliable validation for human biomonitoring. Until now there have not been sufficient data to interpret the relationship between genotypes, biomarkers of exposure, and biomarkers of effect for assessing the risk of human exposure to mutagens and carcinogens.

Monitoring genotoxic exposure in uranium miners.

Recent data from deep uranium mines in Czechoslovakia indicated that in addition to radon daughter products, miners are also exposed to chemical mutagens. Mycotoxins were identified as a possible source of mutagenicity present in the mines. Various methods of biomonitoring were used to examine three groups of miners from different uranium mines. Cytogenetic analysis of peripheral lymphocytes, unscheduled DNA synthesis (UDS) in lymphocytes, and lipid peroxidation (LPO) in both plasma and lymphocytes were studied on 66 exposed miners and 56 controls. Throat swabs were taken from 116 miners and 78 controls. Significantly increased numbers of aberrant cells were found in all groups of miners, as well as decreased UDS values in lymphocytes and increased LPO plasma levels in comparison to controls. Molds were detected in throat swabs from 27% of miners, and 58% of these molds were embryotoxic. Only 5% of the control samples contained molds and none of them was embryotoxic. The following mycotoxins were isolated from miners' throat swab samples: rugulosin, sterigmatocystin, mycophenolic acid, brevianamid A, citreoviridin, citrinin, penicilic acid, and secalonic acid. These data suggest that mycotoxins are a genotoxic factor affecting uranium miners.

Biomarker studies in northern Bohemia.

Studies were conducted in northern Bohemia to simultaneously evaluate personal exposures to air pollution in the form of respirable particles containing polycyclic aromatic hydrocarbons (PAHs) and biomarkers of exposure, biological effective dose, genetic effects, and metabolic susceptibility. The series of biomarkers included PAH metabolites in urine, urine mutagenicity, PAH-DNA adducts in white blood cells determined by 32P-postlabeling, PAH-albumin adducts determined by enzyme-linked immunosorbent assay (ELISA), DNA damage in lymphocytes detected by comet assay, chromosomal aberrations, sister chromatid exchanges, and glutathione S-transferase M1 (GSTM1) genotypes. For these studies, a group of women who work outdoors about 30% of their daily time was selected. In a pilot study, a group of women from a polluted area of the Teplice district (northern Bohemia) was compared with a group of women from a control district of southern Bohemia (Prachatice). In a follow-up repeated-measures study, a group of nonsmoking women from Teplice was sampled repeatedly during the winter season of 1993 to 1994. Personal exposure monitoring for respirable particles (< 2.5 microns) was conducted for the 24-hr period before collection of blood and urine. Particle extracts were analyzed for carcinogenic PAHs. In the pilot study and in the follow-up study, a highly significant correlation between individual personal exposures to PAHs and DNA adducts was found (r = 0.54, p = 0.016; r = 0.710, p < 0.001, respectively). The comet parameter (percentage DNA in tail; %T) correlated with exposures to respirable particles (r = 0.304, p = 0.015). The GSTM1 genotype had a significant effect on urinary PAH metabolites, urine mutagenicity, and comet parameters (% T and tail moment) when the GSTM1 genotype was considered as a single factor affecting these biomarkers. Multifactor analysis o variance considering exposure and adjusting the data for GSTM1, age, and diet showed that the effect of personal exposures to PAHs on the variability of biomarkers (DNA adducts, comet parameters, urine mutagenicity) might be higher than the effect of the GSTM1 genotype. These results show the importance of considering all potential factors that may affect the biomarkers being analyzed.

Teplice program--the impact of air pollution on human health.

The aim of the Teplice Program is to investigate and assess the impact of air pollution on the health of the population in the district of Teplice, Czech Republic. Characterization of the air pollutants demonstrated unusually high concentrations during winter inversions of fine particles dominated by acidic sulfates, genotoxic organic compounds, and toxic trace elements. The major source of airborne fine particles is the burning of coal for heating and power. Human exposure and biomarker studies demonstrated large seasonal variations in air pollution within the Teplice District and higher seasonal average pollution levels than the comparative district, Prachatice. Personal exposures to fine particles and organic carcinogens [e.g., polycyclic aromatic hydrocarbons (PAH)] were correlated with excretion of PAH metabolites in urine, several trace metals in blood, and DNA adducts in white blood cells. Respiratory and neurobehavioral studies of school children were conducted using questionnaires and clinical measures. A significantly higher prevalence of adverse respiratory symptoms and decreased lung function were found in the Teplice district than in Prachatice. The neurobehavioral studies indicated significantly higher teacher referrals for clinical assessment in Teplice, but the majority of objective performance measures did not differ. Reproductive studies were conducted in both males and females. A study of the effects of exposure on pregnancy and birth found an excess prevalence of low birth weight and premature births in Teplice; these adverse effects were more common in infants conceived in the winter and whose mothers were smokers. Based on questionnaires and medical examination, the reproductive development of young men was not different between districts and seasons, however, measures of semen quality suggest that exposure to high levels of air pollution are associated with transient decrements in semen quality.

Influence of GSTM1 and NAT2 genotypes on placental DNA adducts in an environmentally exposed population.

The placenta bulky DNA adducts have been studied in relation to metabolic genotypes for glutathione S-transferase M1 (GSTM1) and N-acetyl transferase 2 (NAT2) in 158 mothers (113 nonsmokers and 45 smokers) living in two regions with different annual average air pollution levels of sulphur dioxide, nitrogen oxides, particulate matter < 10 microns, and polycyclic aromatic hydrocarbons. One region was the district of Teplice as the polluted industrial region with mines and brown coal power plants, and the other was the district of Prachatice, an agricultural region without heavy industry. DNA adduct levels were determined by using a butanol extraction enrichment procedure of 32P-postlabeling. GSTM1 and NAT2 genotypes were studied by using polymerase chain reaction. The total DNA adduct levels included a diagonal radioactive zone (DRZ) and one distinct spot outside DRZ (termed X), which was detected in almost all placenta samples and correlated with DRZ (r = .682; P < .001). We found the total DNA adduct levels 2.12 +/- 1.46 (0.04-7.70) and 1.48 +/- 1.09 (0.11-4.98) adducts per 10(8) nucleotides for Teplice and Prachatice districts, respectively, indicating significant differences between both regions studied (P = .004). Elevated DNA adduct levels were found in smoking mothers (10 or more cigarettes per day) by comparison with nonsmoking mothers (3.21 +/- 1.39 versus 1.32 +/- 0.88 adducts per 10(8) nucleotides; P < .001). Placental DNA adduct levels in smokers correlated with cotinine measured in plasma (r = .432; P = .003). This relation indicates that cigarette smoking could be predominantly responsible for DNA adduct formation in placentas of smoking mothers. DNA adduct levels were evaluated separately for non-smokers (1.50 +/- 1.00 vs. 1.09 +/- 0.66 adducts/10(8) nucleotides for the Teplice and Prachatice districts, respectively; P = .046) and smokers (3.35 +/- 1.47 vs. 2.91 +/- 1.20 adducts/10(8) nucleotides for Teplice and Prachatice districts, respectively; P = .384) to exclude the effect of active cigarette smoking on the district variation. These findings indicate that the effect of the environmental pollution in cigarette smokers is practically overlapped by tobacco exposure. No seasonal variation was observed for DNA adduct levels in the overall population studied and no relation between total DNA adduct levels in placenta and levels of vitamins A, C, and E in venous and cord blood was found. A positive GSTM1 genotype was detected in 78 subjects, while negative GSTM1 genotype was found in 80 subjects. Higher DNA adduct levels were detected in the group with GSTM1-negative genotype by comparison with GSTM1-positive genotype (2.05 +/- 1.30 vs. 1.66 +/- 1.39 adducts/10(8) nucleotides; P = .018). This finding is more pronounced in the Teplice district (2.33 +/- 1.36 vs. 1.88 +/- 1.56 adducts/10(8) nucleotides; P = .053) than for the Prachatice district (1.61 +/- 1.09 vs. 1.36 +/- 1.10 adducts/10(8) nucleotides; P = .248) and for nonsmokers (1.45 +/- 0.82 vs. 1.18 +/- 0.93 adducts/10(8) nucleotides; P = .029) more than for smokers (3.45 +/- 1.14 vs. 2.95 +/- 1.62 adducts/10(8) nucleotides; P = .085). Significant district and seasonal differences were found in subgroups with GSTM1-negative genotype. DNA adduct levels in placentas of the GSTM1-negative subgroup were higher in mothers living in the polluted district of Teplice than in Prachatice (P = .012). The adduct levels in placentas sampled in the summer period were higher than in the winter period in the GSTM1-negative population (P = .006). No effect of the NAT2 genotype on DNA adduct levels was observed.

Stability of benzo[a]pyrene DNA adducts in rat tissues during their long-term storage at -20 degrees C or -80 degrees C.

The aim of this study was to examine whether the storage of tissues at -80 degrees C or -20 degrees C affects the benzo[a]pyrene (B[a]P)-derived DNA adduct pattern and levels in rat tissues. Three rats were treated orally with a single dose of 100 mg B[a]P/kg b.w. and killed 24 h later. White blood cells (WBC) were isolated from the fresh blood. Livers, lungs and hearts were immediately removed, dissected into small fragments and were pooled for each organ. Pooled samples were proportionally divided into 7 aliquots. DNA from the first aliquot was immediately isolated (time 0). The other aliquots were frozen and stored at -20 degrees C or at -80 degrees C. DNA was isolated from the frozen samples at 1, 5 and 10 months later. 32P-postlabeling analysis was performed at the beginning and at the end of study with the whole set of samples. Two B[a]P-derived adducts were detected in all tissues but with different intensities for different tissue types. One of the adducts was found predominantly in WBC (approximately 85%) and liver (approximately 68%), while heart and lung accounted only for approximately 43% and approximately 39%, respectively. This adduct was tentatively identified as benzo[a]pyrene diol-epoxide-N2 adduct (BPDE-N2-dG) based on TLC and HPLC analyses of 32P-postlabeled adducts. The highest total DNA adduct level (sum of 2 spots) was found in lung (4.90 adducts/10(8) nucleotides) compared with heart, liver and WBC (3.55, 2.37 and 2.32 adducts/10(8) nucleotides, respectively). The analysis of variance provided evidence that storage of tissues at -20 degrees C or at -80 degrees C up to 10 months did not significantly affect B[a]P DNA adduct levels and patterns in the rat lung, heart and liver. Our study indicates that properly stored tissues can be used for DNA adduct analysis with confidence.

The effect of paracetamol on oxidative damage in human peripheral lymphocytes.

Unscheduled DNA synthesis (UDSox) and lipid peroxidation (LPO) induced by non-enzymatic activation of molecular oxygen (Fe2+ +H2O2) were measured in human peripheral lymphocytes from healthy volunteers. The effect of paracetamol (PC) in a final concentration range of 0.05-10 mmole/l on these oxidative processes and on DNA repair induced by MNNG (UDSmut) was investigated. The level of induced LPO was measured by the thiobarbituric acid assay, UDSox and UDSmut were determined by scintillometric measurement of incorporated [methyl-3H]thymidine into damaged DNA. PC at concentrations lower than 1 mmole/l significantly potentiates the non-enzymatically induced LPO and UDSox with the maximum of the activation being around 0.1 mmole/l. In contrast, PC at concentrations higher than 1 mmole/l exhibits an inhibitory effect on both LPO and UDSox. On the other hand, concentrations higher than 1 mmole/l significantly suppressed DNA-repair synthesis induced by MNNG.

DNA-repair capacity and lipid peroxidation in chronic alcoholics.

The possible impact of long-term overexposure to ethanol was studied in a group of chronic alcoholics in the psychiatric hospital. The level of DNA methylation and unscheduled DNA synthesis (UDS) induced by N-methyl-N-nitrosourea (MNU) in lymphocytes and lipid peroxidation (LPO) in plasma were used as markers of injury caused by alcohol abuse. The data were correlated with plasma levels of some natural antioxidants (vitamins A, C and E) and vitamin B12. The following results were obtained. The degree of DNA methylation by MNU in lymphocytes was the same in the exposed and control groups under our experimental conditions. The DNA excision-repair capacity of lymphocytes measured as UDS was decreased in alcoholics (p less than 0.01) and LPO in plasma was significantly higher (p less than 0.01) as a consequence of alcohol overconsumption. By the simple regression method, a correlation was found between LPO and vitamin C levels (LPO = -0.078 x vit. C + 1.9; p less than 0.05) and between UDS and LPO values (UDS = -0.384 x LPO + 4.1; p less than 0.05). These results support the hypothesis of a connection of cell membrane status and DNA damage and repair and the possible role of active oxygen species in cell damage caused by ethanol.

32P-postlabeling analysis of DNA adducts in tissues of rats exposed to coke-oven emissions.

Coke-oven workers are occupationally exposed to emissions containing relatively high levels of polycyclic aromatic hydrocarbons. Epidemiological studies suggest that this occupational exposure may lead to an increased risk of lung cancer. To evaluate a biologically effective exposure dose in human biomonitoring studies DNA carcinogen adduct analysis is frequently used. The most readily available source of cellular DNA in these studies is white blood cells (WBC). It is questionable whether WBC are an appropriate surrogate for target tissue cells. In this study an animal model was used to examine the relationship between DNA adduct levels in target tissues and WBC as a surrogate. Rats were exposed to emissions on the top of a coke-oven battery for 24 h during simultaneous sampling of the air for chemical analysis of polycyclic aromatic hydrocarbons. 32P-Postlabeling analysis of DNA adducts in lung, heart, liver and WBC with the butanol enrichment procedure was conducted. DNA adduct profiles differ in target and non-target tissues and WBC analyzed. One major adduct was detected in the DNA from all tissues and WBC analyzed that exhibited the same chromatographic mobility as the predominant B(a)P adduct of the standard DNA sample. The highest levels of this adduct were observed in DNA from lung and heart--16.3 and 12.9 adducts/10(9) nucleotides. The elevation compared to local control animals was 6.8-fold for lung, 8.6-fold for heart, in WBC DNA 3-fold and in liver DNA only 2-fold. In DNA samples from WBC and heart mainly this major adduct was observed. In liver DNA the other four distinct spots outside the diagonal zone (DRZ) and in lung two faster-migrating adducts inside the DRZ with higher intensities were detected. Evaluating total DNA adduct levels, almost the same extent of DNA damage in lung, heart and liver was observed (46.8, 37.7 and 46.2 adducts/10(9) nucleotides; WBC only 6.7 adducts/10(9) nucleotides). Our data showed that DNA injury in target tissue cells caused by exposure to coke-oven emissions may be more significant than expected only according to DNA adduct levels in WBC.

Mutagenicity studies on paracetamol in human volunteers. I. Cytogenetic analysis of peripheral lymphocytes and lipid peroxidation in plasma.

The clastogenic activity of paracetamol (PC) was assayed on a group of 11 healthy volunteers. PC was administered in the form of tablets 3 x 1000 mg in the course of 8 h. Blood samples were taken 0, 24, 72 and 168 h after the first application of the drug. Each blood sample was used for the cytogenetic analysis of peripheral lymphocytes, for the measuring of the level of lipid peroxidation (LPO) and ascorbemia in plasma. After PC administration the frequency of aberrant cells (AB.C.) was increased to 2.77% AB.C. after 24 h vs. 1.68% at 0 h, and breaks per cell (B/C) to 0.0295 vs. 0.0182, respectively. If PC was applied simultaneously with ascorbic acid (AA), also in a dose of 3 x 1000 mg, an increased frequency of AB.C. was observed only after 72 h, of B/C after both 24 h and 72 h. No increase in LPO as determined by the thiobarbituric acid assay was seen after PC administration (1.02-1.10 nmole malondialdehyde (MDA)/ml plasma). The LPO level was increased 72 h after the simultaneous application of PC and AA (1.26 nmole MDA/ml). No effect of AA in terms of a decreased PC clastogenicity was observed.

The influence of alpha-tocopherol and pyritinol on oxidative DNA damage and lipid peroxidation in human lymphocytes.

Unscheduled DNA synthesis (UDS) and lipid peroxidation (LPO) were measured in human peripheral lymphocytes from healthy volunteers. These processes were induced by the catalytic system Fe2+-sodium ascorbate. The degree of induced LPO was measured spectrophotometrically by the thiobarbituric acid assay. UDS was detected by scintillometric measurement of the incorporation of 3H-thymidine into DNA. The protective action by fat-soluble vitamin E (D,L-alpha-tocopherol) and the artificial antioxidant pyritinol on UDS and LPO was also investigated. The system Fe2+ (2 mumole/l)-sodium ascorbate (30 mumole/l) increased the LPO level in healthy volunteers approximately 2.5 times and the incorporation of 3H-thymidine by 60-70%. alpha-Tocopherol (0.2 mmole/l) very efficiently suppressed LPO processes (p less than 0.01) and the oxidative damage of DNA measured as UDS was also significantly diminished (p less than 0.05). Pyritinol had no effect on LPO and UDS under our experimental conditions.

Inhibition of DNA repair synthesis in the rat by in vivo exposure to psychotropic drugs and reversal of the effect by co-administration with alpha-tocopherol.

Changes in unscheduled DNA synthesis (UDS) in lymphocytes and lipid peroxidation (LPO) in the rat brain regions cortex, hippocampus and hypothalamus were studied after 12 months of treatment with the neuroleptic fluphenazine (5 mg/kg b.w.), lithium (0.05% in drinking water), alpha-tocopherol (alpha-TP, 0.01% in drinking water) and the anticholinergic drug 7-methoxytacrine (0.1 and 1.0 g/kg in the diet). Fluphenazine and lithium suppressed UDS and increased LPO in cortex and hypothalamus. 7-Methoxy-tacrine at the lower dose stimulated UDS, at the higher dose it suppressed UDS after 6 months of exposure. Simultaneous administration of alpha-TP with fluphenazine suppressed the increase in LPO and the decrease in UDS produced by the neuroleptic alone. alpha-TP plasma levels were increased in groups administered alpha-TP as well as the levels in the hippocampus. Results indicate that the damage of biomembranes and the DNA repair enzymatic system as a consequence of fluphenazine action may be eliminated by the simultaneous administration of alpha-TP.

The effect of dibenzo[a,1]pyrene and benzo[a]pyrene on human diploid lung fibroblasts: the induction of DNA adducts, expression of p53 and p21(WAF1) proteins and cell cycle distribution.

Polycyclic aromatic hydrocarbons (PAHs) present in ambient air are considered as potential human carcinogens, but the detailed mechanism of action is still unknown. Our aim was to study the in vitro effect of exposure to dibenzo[a,l]pyrene (DB[a,l]P), the most potent carcinogenic PAH ever tested, and benzo[a]pyrene (B[a]P) in a normal human diploid lung fibroblast cells (HEL) using multiple endpoints. DNA adduct levels were measured by 32P-postlabelling, the expression of p53 and p21(WAF1) proteins by western blotting and the cell cycle distribution by flow cytometry. For both PAHs, the DNA adduct formation was proportional to the time of exposure and dependent on the stage of cell growth in culture. DNA binding was detectable even at the lowest concentration used (24h exposure, 0.01 microM for both PAHs). The highest DNA adduct levels were observed after 24h of exposure in near-confluent cells (>90% of cells at G0/G1 phase), but DNA damage induced by DB[a,l]P was approximately 8-10 times higher at a concentration one order of magnitude lower as compared with B[a]P (for B[a]P at 1 microM and for DB[a,l]P at 0.1 microM: 237+/-107 and 2360+/-798 adducts/10(8) nucleotides, respectively). The induction of p53 and p21(WAF1) protein occurred subsequent to the induction of DNA adducts. The DNA adduct levels correlated with both p53 (R=0.832, P<0.001 and R=0.859, P<0.001, for DB[a,l]P and B[a]P, respectively) and p21(WAF1) levels (R=0.808, P<0.001 and R=0.797, P=0.001, for DB[a,l]P and B[a]P, respectively), regardless of the PAH exposure and the phase of cell growth. The results showed that a detectable increase of p53 and p21(WAF1) proteins (> or = 1.5-fold as compared with controls) requires a minimal DNA adduct level of approximately 200-250 adducts/10(8) nucleotides for both PAHs tested and suggest that the level of adducts rather than their structure triggers the p53 and p21(WAF1) responses. The cell cycle was altered after 12-16h of treatment, and after 24h of exposure to 0.1 microM DB[a,l]P in growing cells, there was approximately 24% increase in S phase cells accompanied by a decrease in G1 and G2/mitosis (G2/M) cells. Cell treatment with 1.0 microM B[a]P resulted in more subtle alterations. We conclude that DB[a,l]P, and to a lesser degree B[a]P, are able to induce DNA adducts as well as p53 and p21(WAF1) without eliciting G1 or G2/M arrests but rather an S phase delay/arrest. Whether the S phase delay observed in our study is beneficial for the survival of the cells remains to be further established.

The use of a urine mutagenicity assay in the monitoring of environmental exposure to genotoxins.

Urinary bacterial mutagenicity was used as a biomarker of exposure to ambient air pollution in a group of women working outdoors in the city of Teplice (TP; Northern Bohemia) with higher levels of air pollution than a similar group of women in the city of Prachatice (PT; Southern Bohemia). The Salmonella typhimurium plate incorporation assay with the TA98 and YG1041 strains and microsuspension assay with the YG1041 strain were used for testing the urinary mutagenicity. PAH and their metabolites were analyzed by HPLC and GC/MS methods. The significantly higher values of most PAHs/metabolites detected in a TP group confirmed the differences of PAH exposures between both groups. In the plate incorporation assay, the TA98 strain was not able to detect the increase in urinary mutagenicity, but, for the YG1041 strain, the urinary mutagenicity was clearly determined with a significant difference in number of YG1041 + S9 revertants between the TP and PT groups. The microsuspension assay increased the mean response by about 10-fold over the standard plate test; however, no statistical difference between TP and PT groups was found due to high interindividual variability and small sample size. Comparing the urinary PAH/metabolites to urinary mutagenicity, significant correlations were observed between the plate incorporation mutagenicity results with the YG1041 revertants in the presence of metabolic activation and several of the urinary PAH/metabolites. On the contrary, in the microsuspension assay, several urinary PAH/metabolites correlated significantly with the YG1041 revertants only in the absence of metabolic activation. This may indicate the influence of different treatment conditions of assays on the urinary mutagenicity results. The results suggest the insufficient sensitivity of the TA98 tester strain to determinate low urinary level of mutagens. On the contrary, the use of the YG1041 tester strain increases the probability of detecting an effect of environmental exposure and seems to be applicable to biological monitoring. To definitely replace the standard plate incorporation assay with the microsuspension method is not possible without further comparative studies.