Analysis of oxidative DNA damage after human dietary supplementation with linoleic acid.

It has been hypothesized that oxygen radicals generated by peroxidation of dietary linoleic acid may induce genetic damage and thereby increase cancer risk. We examined the effect of dietary supplementation with linoleic acid on the levels of oxidative DNA damage in peripheral lymphocytes and on the blood plasma antioxidant potential. Thirty volunteers received during 6 weeks either a high dose of linoleic acid (15 g/day), an intermediate dose of linoleic acid (7.5 g/day) or an isocaloric supplement without linoleic acid (15 g palmitic acid/day). After the intervention, no significant increase in oxidative DNA damage, measured as relative amounts of 7,8-dihydro-8-oxo-2'-deoxyguanosine (8-oxodG) in DNA from peripheral lymphocytes, was observed in both high and intermediate linoleic acid-supplemented groups (increase of respectively 13 and 21%; P>0.05). Also, the differences between levels of oxidative DNA damage in the high or intermediate linoleic acid-supplemented group and the control group receiving palmitic acid (23% decrease) were not significant. Furthermore, no statistically significant differences were found between the total antioxidant capacities of blood plasma from the different experimental groups. Plasma levels of malondialdehyde, an important end-product of lipid peroxidation, were not increased after supplementation, nor were effects found on the plasma concentrations of retinol, alpha-tocopherol and beta-carotene. Despite the experimental design that excludes several forms of bias introduced in studies based on modulation of dietary composition, our results provide no indication of increased oxidative stress or genetic damage as a result of increased dietary intake of linoleic acid. Therefore, we see no scientific basis to reconsider the public health policy to stimulate the intake of polyunsaturated fatty acids aimed at the reduction of coronary heart diseases.

A multi-biomarker approach to study the effects of smoking on oxidative DNA damage and repair and antioxidative defense mechanisms.

We investigated the effects of smoking-induced oxidative stress in healthy volunteers (21 smokers versus 24 non-smokers) by quantifying various markers of oxidative DNA damage and repair, and antioxidative defense mechanisms. Lymphocytic 7-hydroxy-8-oxo-2'-deoxyguanosine (8-oxo-dG) levels measured by high performance liquid chromatography with electrochemical detection, were significantly lower in smokers as compared with non-smokers (38.6 +/- 5.2 versus 50.9 +/- 4.6/10(6) dG, P = 0.05). The levels of oxidized pyrimidine bases in lymphocytes of smokers quantified by the endonuclease III-modified comet assay were non-significantly lower than those of non-smokers (% DNA in tail: 13 +/- 3 versus 14 +/- 2; tail length: 69 +/- 13 versus 96 +/- 10; tail moment: 6416 +/- 1220 versus 7545 +/- 1234). Urinary excretion levels of 8-hydroxy-2'-deoxyguanosine (8-OH-dG) assessed by enzyme-linked immunosorbent assay did not differ significantly between smokers and non-smokers (197 +/- 31 versus 240 +/- 33 ng/body mass index, P = 0.3). Overall DNA repair activity expressed as unscheduled DNA synthesis in blood leukocytes, was not significantly different between smokers and non-smokers (2.9 +/- 0.3 versus 3.3 +/- 0.3, P = 0.4). Plasma antioxidative capacity measured by the Trolox equivalent antioxidant capacity assay was slightly higher in smokers as compared with non-smokers (440 +/- 16 versus 400 +/- 15 microM Trolox equivalent, P = 0.09), and it was significantly related to lymphocytic 8-oxo-dG levels (r = 0.4, P = 0.001). Genotyping of human 8-OH-dG glycosylase/apurinic lyase and glutathione S-transferase M1 showed that a polymorphism in either or both of the two genes does not affect any of the quantified biomarkers. We conclude that oxidative stress imposed by cigarette smoking has a low impact upon certain pathways involved in DNA damage and the antioxidative defense system.

Induction of DNA adducts by several polychlorinated biphenyls.

It is known that lower-chlorinated biphenyls are metabolically activated to electrophilic quinoid species capable of binding to DNA. Also, certain metabolites are capable of redox cycling, thereby increasing oxidative stress in biological systems. In the present study, we tested mono-, di-, tri-, tetra-, penta-, hexa-, and heptachlorinated biphenyls for their ability to bind with DNA and to induce oxidative DNA damage. We present additional evidence that several PCB congeners form DNA adducts after metabolic activation, which can be detected by the nuclease P1- or butanol-enrichment procedures of the (32)P-postlabeling technique. Butanol and nuclease P1 enrichments showed different adduct recoveries, depending on the level of chlorination of the biphenyls. Application of the nuclease P1 enrichment showed that the incubation of 2-chloro-; 3, 4-dichloro-; 2,4,4'-trichloro-; 3,4,5-trichloro-; and 2,2',5, 5'-tetrachlorobiphenyl with calf thymus DNA and liver microsomes from rats treated with phenobarbital, followed by oxidation with a peroxidase, produced five to eight different DNA adducts. For these lower-chlorinated biphenyls, butanol enrichment generally showed a lower recovery. For some higher substituted congeners (3,3',4,4', 5-pentachloro-, 2,2',3,4,4',5'-hexachloro-, 2,2',4,4',5, 5'-hexachloro-, and 2,2',3,4,4',5,5'-heptachlorobiphenyl), after butanol enrichment a single dominant spot was observed, which was absent in the nuclease P1 procedure. After incubation of calf thymus DNA with either higher- or lower-chlorinated PCB congeners, we were not able to detect significantly increased levels of oxidative DNA damage above background levels, measured as 8-oxo-7, 8-dihydro-2'deoxyguanosine. In view of the carcinogenicity of PCB mixtures in animals and the ability of PCB metabolites to bind covalently to DNA, rats were orally treated with a mixture of PCBs (Aroclor 1242). PCB-DNA adduct levels were analyzed in PCB target organs: liver, thymus, glandular stomach, spleen, testes, seminal vesicles and prostate DNA. In vivo PCB-DNA adducts could not be detected by either the butanol- or by the NP1-enrichment procedure in rat target tissue DNA. Also, no differences in oxidative DNA damage could be observed between PCB-treated rats and controls. These results indicate a lack of DNA reactivity of PCB mixtures in vivo.

Exposure-route-dependent DNA adduct formation by polycyclic aromatic hydrocarbons.

Understanding the kinetics of aromatic-DNA adducts in target tissues and white blood cells (WBC) would enhance the applicability of DNA adducts in WBC as surrogate source of DNA in biomonitoring studies. In the present study, rats were acutely exposed to benzo[a]pyrene (B[a]P; 10 mg/kg body wt) via intratracheal (i.t.), dermal and oral administration. DNA adducts were analyzed in relevant target organs and WBC by nuclease P1 enriched (32)P-post-labeling at 1, 2, 4, 11 and 21 days after exposure. Additionally, the internal dose was assessed by measurement of urinary excretion of 3-hydroxy-B[a]P (3-OH-B[a]P). Total B[a]P-DNA adduct levels in WBC were highest after i.t. and oral administration, whereas DNA adducts were hardly detectable after dermal exposure. Highest adduct levels were reached at 2 days after exposure. In lung tissue, DNA adduct levels reached maximal values at 2 days and were highest after i.t., oral and dermal exposure, respectively. DNA adduct levels were significantly lower in WBC as compared with lung. Nonetheless, overall B[a]P-DNA adduct levels in WBC were significantly correlated with those in lung. In target organs, highest DNA adduct levels were observed in skin after topical application, and lowest in stomach after oral administration of B[a]P. Furthermore, DNA adduct levels in WBC were correlated with DNA adduct levels in skin after dermal exposure and stomach after oral administration of B[a]P. Two-fold higher levels of 3-OH-B[a]P were excreted after i.t. administration of B[a]P as compared with dermal or oral exposure. Urinary 3-OH-B[a]P concentrations were correlated with DNA adduct levels at the site of B[a]P application. Overall, it can be concluded that aromatic-DNA adduct levels in WBC can be applied as a surrogate source of DNA for the site of application of B[a]P and reflect binding to lung DNA, independently of the exposure route.

Use of crayfish in biomonitoring studies of environmental pollution of the river Meuse.

The river Meuse, located in western Europe, is contaminated by different pollutants, of both organic and inorganic nature. The predominant sources of Meuse contamination in The Netherlands are agricultural activities and pollution derived from urban areas. Crayfish, water, and sediment samples were collected at four different locations of the river Meuse, in order to cover a large part of the catchment area of this river in The Netherlands. Crayfish may be very useful in biomonitoring studies, since they can integrate body load by pollutants over time in an area-bound manner. In these crayfish, levels of aromatic DNA adducts, heavy metal residues, polychlorinated biphenyls (PCBs), and organochlorine pesticides were determined in hepatopancreatic tissue. Also analyzed were water and sediment samples derived from the same locations, for polycyclic aromatic hydrocarbons (PAHs), heavy metals, and organochlorine compounds. In sediments from the four different sampling sites, no clear differences were observed in PCB levels. Organochlorine pesticide concentrations were highest at location A, the most upstream sampling site, whereas a general decrease was observed following the river Meuse downstream. A similar pattern was observed for the metal compounds. For PAH sediment levels no consistent tendency could be observed. Highest values were detected at site B, followed by, respectively, locations A, D, and C. In water samples, a different pattern was observed. The highest metal concentration was observed at location D, whereas the total organochlorine level was higher at sites B and D, compared to the two other sampling sites. Differences in pollution levels in crayfish between sampling sites were evident. Site D, the most downstream-situated site examined, appeared to be the most polluted site with respect to PCBs, DDT, DDE, and Cu in crayfish. Moreover, DNA adduct levels, which may serve as a dosimeter for the internal dose of aromatic compounds such as PAHs and PCBs, were also significantly higher in hepatopancreatic tissue of crayfish captured at site D, compared to the three other sampling sites. Moreover, significant correlations were observed between DNA adduct levels and the lower chlorinated PCB congeners (PCB 28-PCB 101). By correlating the different pollutants in water and/or sediment with xenobiotic levels in crayfish, no consistency could be observed, indicating that monitoring aquatic species may provide specific information on the presence of surface water pollutants. These results indicate that crayfish can be used as biological indicators of exposure to both organic and inorganic pollution in aquatic systems.

In vitro effects of coal fly ashes: hydroxyl radical generation, iron release, and DNA damage and toxicity in rat lung epithelial cells.

Oxygen radical generation due to surface radicals, inflammation, and iron release has been suggested as the mechanism of adverse effects of quartz, such as emphysema, fibrosis, and carcinogenic effects. Therefore, we measured iron release, acellular generation of hydroxyl radicals, and oxidative DNA damage and cytotoxicity in rat lung epithelial (RLE) cells by different coal fly ashes (CFA) that contain both quartz and iron. Seven samples of CFA with different particle size and quartz content (up to 14.1%) were tested along with silica (alpha-quartz), ground coal, and coal mine dust (respirable) as positive control particles, and fine TiO(2) (anatase) as a negative control. Five test samples were pulverized fuel ashes (PFA), two samples were coal gasification (SCG) ashes (quartz content <0.1%), and one sample was a ground coal. No marked differences between SCG and PFA fly ashes were observed, and toxicity did not correlate with physicochemical characteristics or effect parameters. Stable surface radicals were only detected in the reference particles silica and coal mine dust, but not in CFA. On the other hand, hydroxyl radical generation by all fly ashes was observed in the presence of hydrogen peroxide, which was positively correlated with iron mobilization and inhibited by deferoxamine, but not correlated with iron or quartz content. Also a relationship between acellular hydroxyl radical generation and oxidative DNA damage in RLE cells by CFA was observed. Differences in hydroxyl radical generation and oxidative damage by the CFA were not related to iron and quartz content, but the respirable ashes (MAT023, 38, and 41) showed a very extensive level of hydroxyl radical generation in comparison to nonrespirable fly ashes and respirable references. This radical generation was clearly related to the iron mobilization from these particles. In conclusion, the mechanisms by which CFA and the positive references (silica, coal mine dust) affect rat lung epithelial cells seem to be different, and the data suggest that quartz in CFA does not act the same as quartz in silica or coal mine dust. On the other hand, the results indicate an important role for size and iron release in generation and subsequent effects of reactive oxygen species caused by CFA.

Neutrophils cause oxidative DNA damage in alveolar epithelial cells.

Inflammation has been recognized as a contributing factor in the pathogenesis of some cancers. In the lung, inflammation is characterized by an influx of polymorphonuclear leukocytes (PMN) that release a variety of reactive oxygen species (ROS). The aim of the present study was to investigate the direct effect of PMN on oxidative DNA damage in lung target cells. Therefore, rat alveolar epithelial cells (RLE) were coincubated with PMN or hydrogen peroxide. Known to be correlated with the incidence of cancer, 7-hydro-8-oxo-2'deoxyguanosine (8-oxodG) was used as an effect marker for oxidative damage. Viability of the RLE, when coincubated with PMN, decreased to 43%, dependent on the ratio between PMN and RLE. After washing off PMN, 8-oxodG levels were significantly increased in RLE, but the highest levels were observed in the washed off PMN fraction. In addition, to avoid washing off procedures, immunohistochemical analysis was used to measure the 8-oxodG levels specifically in the RLE and similar results were obtained. In addition, inhibitor experiments showed that antioxidants ameliorated oxidative DNA damage. Our data provide evidence that ROS released by PMN as well as H2O2, cause oxidative DNA damage in epithelial cells.

Analysis of oxidative DNA damage and HPRT mutant frequencies in cancer patients before and after radiotherapy.

Various markers of radiation-induced DNA damage including DNA oxidation were investigated in peripheral lymphocytes of 23 cancer patients prior to and one week after receiving radiotherapy with a cumulative dose of 54-70 Gy. Exposure to ionizing radiation nonsignificantly increased the ratio 2'deoxy-7-dihydro-8-oxoguanosine/2'deoxyguanosine (8-oxodG/dG) from 1.73 x 10(-5) to 3.33 x 10(-5). Frequencies of micronuclei significantly (p = 0.0003) increased from 6.4 to 38.9 per 1000 cells. The frequency of hypoxanthine-guanine-phosphoribosyltransferase (HPRT) mutant lymphocytes measured as 6-thioguanine resistant variant cells by 5-bromodeoxyuridine labeling, was elevated eight-fold, from 4.7 x 10(-6) to 36.2 x 10(-6) (p = 0.008) after termination of the radiotherapy, thus showing a clear response to the radiation treatment. No correlation between levels of oxidative DNA damage and frequencies of HPRT mutant lymphocytes or micronuclei could be established.

Oxidative DNA damage and cytogenetic effects in flight engineers exposed to cosmic radiation.

This study set out to analyze biomarkers for genotoxic events, e.g., oxidative DNA damage, chromosomal damage and hprt mutations, among flight personnel, who are known to be occupationally exposed to ionizing radiation of cosmic origin. Twenty-three flight engineers were recruited while ground personnel served as a matched control group. Cumulative radiation doses during flight were calculated on the basis of subjects' flight records assuming an exposure rate of 6 microSv per hour of flight. Oxidative DNA damage in peripheral lymphocytes from flight engineers appeared significantly increased in comparison with controls and was associated with cumulative exposure to cosmic radiation. Frequencies of peripheral lymphocyte chromosome aberrations, micronuclei and hprt mutations appeared also to be increased in flight engineers, but not significantly. It was also observed that DNA damage was higher in flight engineers with a relatively shorter flight history in comparison with flight engineers with higher cumulative exposures to radiation, suggesting adaptation to DNA damage caused by ionizing radiation. DNA repair activities measured as unscheduled DNA synthesis were clearly increased in the higher-exposed subgroup of flight engineers, and appeared significantly correlated with cumulative radiation dose, as well as inversely with oxidative DNA damage. The implications for cancer risk assessment in relation to exposure to cosmic radiation are discussed.

Comparison of 32P-postlabeling and HPLC-FD analysis of DNA adducts in rats acutely exposed to benzo(a)pyrene.

DNA adduct analysis is often used for biomonitoring individuals exposed to polycyclic aromatic hydrocarbons (PAH). The 32P-postlabeling assay is routinely applied to study the formation of aromatic bulky adducts, but cannot positively identify individual adduct types. Recently, an HPLC assay with fluorescence detection (HPLC-FD) was developed which was sufficiently sensitive to detect adducts formed by benzo[a]pyrene (B[a]P) diolepoxide isomers [(+/-)anti- and (+/-)syn-BPDE] in occupationally exposed subjects (Rojas et al. Carcinogenesis, 16 (1995) 1373-1376). In this study, we compared both techniques using DNA samples of rats which were treated i.p. with B[a]P (10 mg/kg bw). The internal dose was assessed by measuring 3-OH-B[a]P excretion in urine. The detection limit of the HPLC-FD assay varied from 0.5 to 7.4 adducts per 10(8) nucleotides, while the detection limit of the 32P-postlabeling assay was around 1 adduct per 10(9) nucleotides. HPLC-FD analysis showed that BPDE-DNA adduct levels were highest in the heart, lung and liver respectively. The most predominant B[a]P-tetrol was the I-1 isomer, which derives from hydrolysis of the major reaction product of DNA and (+)-anti-BPDE. 32P-postlabeling analysis revealed an adduct spot that comigrated with a [3H]BPDE-DNA standard. The putative BPDE-DNA adduct levels were highest in heart followed by lung and liver and correlated significantly with tetrol I-1 levels determined by HPLC-FD (r = 0.72, P = 0.006). In samples in which both tetrol I-1 and II-2 were detected by means of HPLC-FD, this correlation was even better (r = 0.95, P = 0.01). Estimated half-lives of BPDE-DNA adducts were in the ranking order; heart, lung and liver for both techniques. By 32P-postlabeling, adducts other than BPDE-DNA were also found, resulting in highest total DNA adduct levels in the liver, heart and lung respectively. Furthermore, mean 24 h urinary excretion of 3-OH-B[a]P was related to BPDE-DNA adduct levels in lung, liver and heart. The 32P-postlabeling assay is sensitive and capable of detecting exposures to complex mixtures, whereas the HPLC-FD assay can be used to identify BPDE-isomers and might therefore be of value in risk assessment of individuals exposed to PAH.