Endogenous and background DNA adducts by methylating and 2-hydroxyethylating agents

Detection of 7-alkylguanine DNA adducts is useful to assess human exposure to and the resulting DNA damage caused by simple alkylating agents. The background 7-methylguanine (7-MG) and 7-hydroxyethylguanine (7-HEG) adduct levels were determined in human and rat tissues, using thin-layer chromatography (TLC) combined with high pressure liquid chromatography (HPLC). In addition, these two adduct levels were also compared in various tissues between smokers and non-smokers. The results demonstrated that the background level of 7-alkylguanine adducts in WBC and lung tissues of non-smokers was 2.9 and 4.0 adducts/107 nucleotides, respectively. In smokers with lung cancers 7-MG adduct level in lung samples (6.3+/-1.9 adducts/107 nucleotides) and in bronchus samples (6.1+/-1.5 adducts/107 nucleotides) was significantly higher than that in WBC samples (3.3+/-0.9 adducts/107 nucleotides). 7-HEG adduct levels obtained from the same individuals were 0.8+/-0.3 in lung, 1.0+/-0.8 in bronchus and 0.6+/-0.2 adducts/107 nucleotides in WBC, respectively. Animal studies showed that background levels of 7-MG (2.1-2.5 adducts/107 nucleotides) in control rats were approximately 2-4-fold higher than 7-HEG levels (0.6-0.9 adducts/107 nucleotides). After a 3-day exposure to 300 ppm ethene, 7-HEG adducts accumulated to a similar extent in different tissues of rats, with the mean adduct level of 5.6-7.0 in liver, 7.4 in lymphocytes and 5.5 adducts/107 nucleotides in kidney.     

DNA damage and repair in gastric cancer--a correlation with the hOGG1 and RAD51 genes polymorphisms

Aristolochic acid (AA) is a potent nephrotoxin and carcinogen and is the causative factor for Chinese herb nephropathy. AA has been associated with the development of urothelial cancer in humans, and kidney and forestomach tumors in rodents. To investigate the molecular mechanisms responsible for the tumorigenicity of AA, we determined the DNA adduct formation and mutagenicity of AA in the liver (nontarget tissue) and kidney (target tissue) of Big Blue rats. Groups of six male rats were gavaged with 0, 0.1, 1.0 and 10.0 mg AA/kg body weight five times/week for 3 months. The rats were sacrificed 1 day after the final treatment, and the livers and kidneys were isolated. DNA adduct formation was analyzed by ³²P-postlabeling and mutant frequency (MF) was determined using the λ Select-cII Mutation Detection System. Three major adducts (7-[deoxyadenosin-N⁶-yl]-aristolactam I, 7-[deoxyadenosin-N⁶-yl]-aristolactam II and 7-[deoxyguanosin-N²-yl]-aristolactam I) were identified. There were strong linear dose-responses for AA-induced DNA adducts in treated rats, ranging from 25 to 1967 adducts/10⁸ nucleotides in liver and 95–4598 adducts/10⁸ nucleotides in kidney. A similar trend of dose-responses for mutation induction also was found, the MFs ranging from 37 to 666 × 10⁻⁶ in liver compared with the MFs of 78–1319 × 10⁻⁶ that we previously reported for the kidneys of AA-treated rats. Overall, kidneys had at least two-fold higher levels of DNA adducts and MF than livers. Sequence analysis of the cII mutants revealed that there was a statistically significant difference between the mutation spectra in both kidney and liver of AA-treated and control rats, but there was no significant difference between the mutation spectra in AA-treated livers and kidneys. A:T → T:A transversion was the predominant mutation in AA-treated rats; whereas G:C → A:T transition was the main type of mutation in control rats. These results indicate that the AA treatment that eventually results in kidney tumors in rats also results in significant increases in DNA adduct formation and cII MF in kidney. Although the same treatment does not produce tumors in rat liver, it does induce DNA adducts and mutations in this tissue, albeit at lower levels than in kidney.     

Dose responses for DNA adduct formation in tissues of rats and mice exposed by inhalation to low concentrations of 1,3-[2,3-[(14)C]-butadiene

Male Sprague-Dawley rats and B6C3F1 mice were exposed to either a single 6h or a multiple (5) daily (6h) nose-only dose of 1,3-[2,3-(14)C]-butadiene at exposure concentrations of nominally 1, 5 or 20 ppm. The aim was to compare the results with those from a similar previous study at 200 ppm. DNA isolated from liver, lung and testis of exposed rats and mice was analysed for the presence of butadiene related adducts, especially the N7-guanine adducts. Total radioactivity present in the DNA from liver, lung and testis was quantified and indicated more covalent binding of radioactivity for mouse tissue DNA than rat tissue DNA. Following release of the depurinating DNA adducts by neutral thermal hydrolysis, the liberated depurinated DNA adducts were measured by reverse phase HPLC coupled with liquid scintillation counting. The guanine adduct G4, assigned as N7-(2,3,4-trihydroxybutyl)- guanine, was the major adduct measured in liver, lung and testis DNA in both rats and mice. Higher levels of G4 were detected in all mouse tissues compared with rat tissue. The dose-response relationship for the formation of adduct G4 was approximately linear for all tissues studied for both rats and mice exposed in the 1-20 ppm range. The formation of G4 in liver tissue was about three times more effective for mouse than rat in this exposure range. Average levels of adduct G4 measured in liver DNA of rats and mice exposed to 5 x 6 h 1, 5 and 20 ppm 1,3-[2,3-(14)C]-butadiene were, respectively, for rats: 0.79 +/- 0.30, 2.90 +/- 1.19, 16.35 +/- 4.8 adducts/10(8) nucleotides and for mice: 2.23 +/- 0.71, 12.24 +/- 2.15, 48.63 +/- 12.61 adducts/10(8) nucleotides. For lung DNA the corresponding values were for rats: 1.02 +/- 0.44, 3.12 +/- 1.06, 17.02 +/- 4.07 adducts/10(8) nucleotides, and for mice: 3.28 +/- 0.32, 14.04 +/- 1.55, 42.47 +/- 13.12 adducts/10(8) nucleotides. Limited comparative data showed that the levels of adduct G4 formed in liver and lung DNA of mice exposed to a single exposure to butadiene in the present 20 ppm study and earlier 200 ppm study were approximately directly proportional across dose, but this was not observed in the case of rats. From the available evidence it is most likely that adduct G4 was formed from a specific isomer of the diol-epoxide metabolite, 3,4-epoxy-1,2-butanediol rather than the diepoxide, 1,2,3,4-diepoxybutane. Another adduct G3, possibly a diastereomer of N7-(2,3,4-trihydroxybutyl)-guanine or most likely the regioisomer N7-(1-hydroxymethyl-2,3-dihydroxypropyl)-guanine, was also detected in DNA of mouse tissues but was essentially absent in DNA from rat tissue. Qualitatively similar profiles of adducts were observed following exposures to butadiene in the present 20 ppm study and the previous 200 ppm study. Overall the DNA adduct levels measured in tissues of both rats and mice were very low. The differences in the profiles and quantity of adducts seen between mice and rats were considered insufficient to explain the large difference in carcinogenic potency of butadiene to mice compared with rats.     

Modification of DNA by mitomycin C in cancer patients detected by 32P-postlabeling analysis

DNA adducts of mitomycin C (MMC) were detected by 32P-postlabeling analysis in both surgical specimens and an autopsy sample of the liver of patients with hepatocellular carcinoma who had received chemotherapy with MMC. Four kinds of adducts were detected in all 6 patients treated with MMC. These adducts had identical chromatographic mobilities to those of adducts in the liver of rats treated with MMC, but 1 additional adduct was detected in rat liver. In patients treated with MMC, about 3 adducts/10(8) nucleotides were found 4 days after MMC treatment, and 1 adduct/10(8) nucleotides 14 days after treatment and the latter level was maintained for up to 56 days. MMC-DNA adducts were also detected in peripheral blood leukocytes from a patient 1 and 7 days after MMC treatment, at levels of 1 and 0.6 adduct/10(8) nucleotides, respectively. These results suggest the tumor-initiating activity of MMC in humans.     

DNA adducts of styrene-7,8-oxide in target and non-target organs for tumor induction in rat and mouse after repeated inhalation exposure to styrene

Styrene by inhalation had been shown to increase the lung tumor incidence in mice at 20 ppm and higher, but was not carcinogenic in rats at up to 1000 ppm. Styrene-7,8-oxide, the major metabolic intermediate, has weak electrophilic reactivity. Therefore, DNA adduct formation was expected at a low level and a 32P-postlabeling method for a determination of the two regioisomeric 2'-deoxyguanosyl-O6-adducts at the alpha(7)- and beta(8)-positions had been established. The first question was whether DNA adducts could be measured in the rat at the end of the 2 years exposure of a bioassay for carcinogenicity, even though tumor incidence was not increased. Liver samples of male and female CD rats were available for DNA adduct analysis. Adducts were above the limit of detection only in the highest dose group (1000 ppm), with median levels of 9 and 8 adducts per 10(7) nucleotides in males and females, respectively (sum of alpha- and beta-adducts). The result indicates that the rat liver tolerated a relatively high steady-state level of styrene-induced DNA adducts without detectable increase in tumor formation. The second question was whether different DNA adduct levels in the lung of rats and mice could account for the species difference in tumor incidence. Groups of female CD-1 mice were exposed for 2 weeks to 0, 40, and 160 ppm styrene (6h per day; 5 days per week), female CD rats were exposed to 0 and 500 ppm. In none of the lung DNA samples were adducts above a limit of detection of 1 adduct per 10(7) DNA nucleotides. The data indicate that species- and organ-specific tumor induction by styrene is not reflected by DNA adduct levels determined in tissue homogenate. The particular susceptibility of the mouse lung might have to be based on other reactive metabolites and DNA adducts, indirect DNA damage and/or cell-type specific toxicity and tumor promotion.     

Formation of DNA adducts and induction of mutagenic effects in rats following 4 weeks inhalation exposure to ethylene oxide as a basis for cancer risk assessment

Ethylene oxide (EO) is mutagenic in various in vitro and in vivo test systems and carcinogenic in rodents. EO forms different adducts upon reaction with DNA, N7-(2-hydroxyethyl)guanine (N7-HEG) being the main adduct. The major objectives of this study were: (a) to determine the formation and persistence of N7-HEG adducts in liver DNA of adult male rats exposed to 0, 50, 100 and 200 ppm by inhalation (4 weeks, 5 days/week, 6 h/day) and (b) to assess dose-response relationships for Hprt gene mutations and various types of chromosomal changes in splenic lymphocytes.N7-HEG adducts were measured 5, 21, 35 and 49 days after cessation of exposure. By extrapolation, the mean concentrations of N7-HEG immediately after cessation of exposure ('day 0') to 50, 100 and 200 ppm were calculated as 310, 558 and 1202 adducts/10(8) nucleotides, respectively, while the mean concentration in control rats was 2.6 adducts/10(8) nucleotides. At 49 days, N7-HEG values had returned close to background levels. The mean levels of N-(2-hydroxyethylvaline) adducts in haemoglobin were also determined and amounted 61.7, 114 and 247 nmol/g globin, respectively. Statistically significant linear relationships were found between mean N7-HEG levels ('day 0') and Hprt mutant frequencies at expression times 21/22 and 49/50 days and between mean N7-HEG ('day 0') and sister-chromatid exchanges (SCEs) or high frequency cells (HFC) measured 5 days post-exposure. At day 21 post-exposure, SCEs and HFCs in-part persisted and were significantly correlated with persistent N7-HEG adducts. No statistically significant dose effect relationships were observed for induction of micronuclei, nor for chromosome breaks or translocations.In conclusion, this study indicates that following sub-chronic exposure, EO is only weakly mutagenic in adult rats. Using the data of this study to predict cancer risk in man resulting from low level EO exposures in conjunction with other published data, i.e., those on (a) genotoxic effects of EO in humans and rats, (b) DNA binding of other carcinogens, (c) natural background DNA binding and (d) genotoxic potency of low energy transfer (LET) radiation, it is not expected that long term occupational exposure to airborne concentrations of EO at or below 1 ppm EO produces an unacceptable increased risk in man.     

Relative sensitivity of 32P-postlabelling of DNA and the autoradiographic UDS assay in the liver of rats exposed to 2-acetylaminofluorene (2AAF)

Groups of male Alderley Park rats were dosed concomitantly with 2-acetylaminofluorene (2AAF) by gavage at doses between 0.01 mg/kg and 40 mg/kg, and livers sampled 2-72 h later. The liver of one group of animals was perfused to yield hepatocytes which were assayed in vitro for unscheduled DNA synthesis (UDS) via incorporation of tritiated thymidine and autoradiography. DNA was extracted from the livers of the other group and DNA adduct levels determined using the 32P-postlabelling technique. The major C-8 2-aminofluorene/guanosine adduct and 3 minor adducts were quantitated, enabling the relative sensitivity of the 2 techniques to be compared. A dose- and time-related UDS response was observed, which, at the most sensitive time-point (12 h) enabled DNA repair to be discerned at a dose level of 0.1-1 mg/kg of 2AAF, a response classified as formally positive at 5 mg/kg 2AAF. Only the C-8 adduct, as determined by 32P-postlabelling, was discernible at 0.01 mg/kg of 2AAF, although other adducts were visible on autoradiograms at higher dose levels. It is concluded that as part of a well-defined dose response, UDS can be discerned with confidence for doses of 2AAF between approximately 0.1 and 5 mg/kg, and DNA adducts for doses of 2AAF between approximately 0.01 and 1 mg/kg. Discernible UDS for 2AAF in the rat liver is apparent at approximately 13 DNA (total) adducts/10(8) nucleotides, or approximately 8 DNA (C-8) adducts/10(8) nucleotides. The presumed C-8 2-acetylaminofluorene/guanosine adduct, prepared by reaction of 2-acetoxy-2-acetylaminofluorene (2AAAF) with DNA, was a significant but unreliable marker of 2AAF/DNA adducts in the rat liver in vivo. DNA repair did not appear to remove DNA adducts selectively, and adducts remained in DNA when discernible DNA repair had ceased.     

Correlation of DNA adduct levels with tumor incidence: carcinogenic potency of DNA adducts

The quantitative relationship between DNA adducts and tumor incidence is evaluated in this review. All available data on DNA adduct levels determined after repeated administration of a carcinogen to rats or mice have been compiled. The list comprised 27 chemicals, of all major structural classes of carcinogens. For the correlation with tumor incidence, the DNA adduct levels measured at the given dose were normalized to the dose which resulted in a 50% tumor incidence under the conditions of a 2-year bioassay (TD50 dose). In rat liver, the calculated adduct concentration 'responsible' for a 50% hepatocellular tumor incidence spanned from 53 to 2083 adducts per 108 nucleotides, for aflatoxin B1, tamoxifen, IQ, MeIQx, 2,4-diaminotoluene, and dimethylnitrosamine (in this order). In mouse liver, the respective figures were 812 to 5543 adducts per 108 nucleotides, for ethylene oxide, dimethylnitrosamine, 4-aminobiphenyl, and 2-acetylaminofluorene. The observed span (40-fold in rats, 7-fold in mice) reflects differences between the various DNA adducts to lead to critical mutations. If additional carcinogens fit in with this astonishingly narrow range, the measurement of DNA adduct levels in target tissue has the potential to be not only an exposure marker but an individual cancer risk marker. For toremifen and styrene, low levels of DNA adducts were detected in rat liver at the end of a negative long-term bioassay. This shows that the limit of detection of DNA adducts can be well below the limit of detection of an increased tumor incidence. For a cancer risk assessment at low levels of DNA damage, treatment-related adducts must be discussed in relation to the background DNA damage and its inter- and intraindividual variability.     

DNA adduct formation and persistence in liver and extrahepatic tissues of northern pike (Esox lucius) following oral exposure to benzo[a]pyrene, benzo[k]fluoranthene and 7H-dibenzo[c,g]carbazole.

The formation and persistence of DNA adducts in liver, intestinal mucosa, gills and brain of juvenile northern pike (Esox lucius) following oral exposure to benzo[a]pyrene (BaP), benzo[k]fluoranthene (BkF) and 7H-dibenzo[c,g]carbazol (DBC) were analysed by 32P-postlabelling. The dosage was 25 micromol/kg body weight of each substance, administered on 5 occasions with an interval of 12-14 days. Sampling was carried out 9 days after the second treatment, and 9, 16, 33 and 78 days after the fifth treatment. Pikes were also fed with the substances singly for comparison of adduct patterns. A complex pattern of adducts was detected in all examined tissues from fish treated with the mixture. Total adduct levels were highest in intestine (347+/-17.4 nmol adducts/mol nucleotides, mean+/-SE), followed by liver (110+/-9.3), gills (69+/-6) and brain (14+/-4.2). In pike treated with BaP alone, one major adduct was detected in all examined tissues. This BaP-adduct made up approximately 50% of the total amount of adducts in the brain. Corresponding values in liver, intestine and gills were 23, 31 and 34%, respectively. One relatively weak BkF-adduct and at least 10 different DBC-adducts were detected in all analysed tissues. Total adduct level in the intestine declined to 29.4% of the maximum value 78 days after the last exposure, while there was no significant decline in adduct levels in liver, gills or brain. The results suggest that intestine is more susceptible to adduct formation than liver after oral exposure, and that adduct levels in the intestine represent ongoing or relatively recent exposure. DNA adducts in the other investigated tissues were much more persistent and may therefore accumulate during long-term exposure.     

32P-postlabelling analysis of DNA adducts from Fischer-344 rats administered 2,4-diaminotoluene.

Using 32P-postlabelling and thin layer chromatography, DNA adduct formation by the potent animal carcinogen 2,4-diaminotoluene in Fischer-344 rats was investigated. DNA from four different organs, liver, mammary gland, kidney and lung, were examined for adducts following single administration of this compound. DNA binding was detected in all four organs, with each producing one major and two minor adduct spots on autoradiograms. The adducts induced were qualitatively identical among the different organs, but quantitative differences were observed. The two target organs of 2,4-diaminotoluene induced carcinogenesis, the liver and mammary gland produced higher adduct yields, with levels up to 30-times higher than those for the two non-target organs. Since the liver is the principal target for 2,4-diaminotoluene induced carcinogenesis, we further examined DNA adducts from this site for the effects of different doses and time points. DNA binding in liver was detected following doses as low as 4.1 mumol/kg. At the highest concentration examined (2046 mumol/kg), the level of the major adduct was 29.2 adducted nucleotides per 10(7) total nucleotides. The yields for the two minor adducts were approximately one-tenth that for the major adduct. Following a 410 mumol/kg dose, DNA adduct removal over time was examined. DNA adduct removal exhibited biphasic kinetics, with a rapid initial phase followed by a slower rate of elimination. Up to 60% of maximum adduct levels persisted after 2 weeks. DNA binding by 2,4-diaminotoluene was also compared to that by its weakly carcinogenic analog, 2,4-dinitrotoluene. The two compounds produced identical adduct patterns, suggesting that they share common metabolites and adducts. Adduct yields from 2,4-dinitrotoluene, however, were lower. The results of our studies suggest that the differences in carcinogenic potency between 2,4-diaminotoluene and 2,4-dinitrotoluene, as well as the organotropic effects of 2,4-diaminotoluene may be explained, in part, by quantitative differences in the extent of DNA adduct formation.     

Further evidence that eugenol does not bind to DNA in vivo

The naturally-occurring alkenylbenzene, eugenol, was examined for its ability to form DNA adducts in the livers of mice that had been treated with up to 10 mg of the compound. No adducts were detected by 32P-postlabelling with a limit of detection of 1 adduct in 10(9) nucleotides. Under these conditions adducts were readily detected in liver DNA from the structurally-related hepatocarcinogen safrole.     

Biomarkers of marine pollution observed in species of mullet living in two eastern Mediterranean harbours

The activities of enzymes associated with xenobiotic metabolism and or oxidative processes, and the levels of aromatic DNA adducts, have been determined in the livers of grey mullet Oedalechilus labeo and Lisa ramada living in two eastern Mediterranean harbours. Glutathione peroxidase GSH P activity was 2.5 times higher 9 IU g-1 liver and glutathione reductase GSSG R activity was twice as high 2.5 IU g-1 liver in fish from the more polluted harbour at Mersin than in the harbour near Erdemli. Superoxide dismutase SOD activity was 25 lower 4.3 IU g-1 liver in the more polluted harbour. The concentrations of glutathione and malondialdehyde varied both with species and environment by a factor of 2.5-3. DNA adducts in liver were determined by 32P postlabelling. In Oedalechilus labeo in the more polluted harbour, adduct levels were 258 21 adducts per 108 nucleotides mean SE; two groups of Lisa ramada were distinguished having 261 48 and 30 6 adducts per 108 nucleotides, respectively. The average adduct level in a group of mullet of mixed species in the less polluted harbour was 3.3 2.3 adducts per 108 nucleotides. The results illuminate the ability of mullet to live in contaminated marine environments, and show that enzyme activities and liver DNA adduct levels can serve as indicators of marine pollution.     

Biomarkers of marine pollution observed in species of mullet living in two eastern Mediterranean harbours

The activities of enzymes associated with xenobiotic metabolism and or oxidative processes, and the levels of aromatic DNA adducts, have been determined in the livers of grey mullet Oedalechilus labeo and Lisa ramada living in two eastern Mediterranean harbours. Glutathione peroxidase GSH P activity was 2.5 times higher 9 IU g-1 liver and glutathione reductase GSSG R activity was twice as high 2.5 IU g-1 liver in fish from the more polluted harbour at Mersin than in the harbour near Erdemli. Superoxide dismutase SOD activity was 25 lower 4.3 IU g-1 liver in the more polluted harbour. The concentrations of glutathione and malondialdehyde varied both with species and environment by a factor of 2.5-3. DNA adducts in liver were determined by 32P postlabelling. In Oedalechilus labeo in the more polluted harbour, adduct levels were 258 21 adducts per 108 nucleotides mean SE ; two groups of Lisa ramada were distinguished having 261 48 and 30 6 adducts per 108 nucleotides, respectively. The average adduct level in a group of mullet of mixed species in the less polluted harbour was 3.3 2.3 adducts per 108 nucleotides. The results illuminate the ability of mullet to live in contaminated marine environments, and show that enzyme activities and liver DNA adduct levels can serve as indicators of marine pollution.     

Regio and stereospecific DNA adduct formation in mouse lung at N6 and N7 position of adenine and guanine after 1,3 butadiene inhalation exposure

Butadiene monoepoxide (BMO) alkylated guanine N7 and adenine N 6 adducts were prepared and enriched by solid phase extraction and HPLC. The purified adducts were analysed by a modified 32P-postlabelling assay, which utilized one dimensional TLC chromatography and a subsequent HPLC analysis with UV and radioactivity detectors. In vitro with Ct-DNA the formation of N7-dGMP and N 6-dAMP adducts were linear at a concentration range of 44 to 870 nmol of BMO per mg DNA at physiological pH. N7- dGMP and N 6-dAMP adducts were formed in a ratio of 200:1. In dGMP and in dAMP 48 % and 86 % of adducts were covalently bound to the C-2 carbon of BMO. CD-1 mice were inhalation exposed to butadiene for 5 days and 6 h per day. The N7-dGMP adduct level in lung samples of animals exposed to 200, 500 and 1300 ppm was 2.8 +/- 0.9 fmol, 11 +/- 2.0 fmol and 30 +/- 6.7 fmol in 10 mug DNA, respectively. The level of N 6-dAMP adducts in lung samples after 500 ppm and 1300 ppm exposure was 0.09 +/- 0.06 fmol and 0.11 +/- 0.05 fmol in 10 mug DNA. At 200 ppm the adduct level was below the detection limit. A sub-group of animals exposed to 1300 ppm was killed 3 weeks after the last exposure. N7-dGMP adducts were not detected but the level of N 6-dAMP adducts was not affected. N7-dGMP adducts were formed in a clear stereospecific manner in vivo . S -BMO adducts were the main product and represented 77 % ( n = 4, SD = 2%) of total BMO adducts. No clear conclusion can be drawn about the enantiospecific DNA binding at the N 6 position of dAMP, because of the poor separation of the enantiomers. However, we could separate regioisomeric adducts which indicated that C-2 adducts represented 69 +/- 3 % of the total N 6 adducts formed in mice lung DNA. This observation is supported by the data derived from in vitro DNA experiments but is different to our previously published data, which indicates the 2:1 (C-1:C-2) ratio in regioisomer formation in nucleotides or nucleosides. We suggest that the data presented in this communication indicate a different mechanism between nucleotides and DNA in BMO-derived adduct formation- Dimroth rearrangement dominates in nucleotides, but in double stranded DNA a direct alkylation is probably the major mechanism of adduct formation.     

Regio and stereospecific DNA adduct formation in mouse lung at N6 and N7 position of adenine and guanine after 1,3 butadiene inhalation exposure

Butadiene monoepoxide (BMO) alkylated guanine N7 and adenine N 6 adducts were prepared and enriched by solid phase extraction and HPLC. The purified adducts were analysed by a modified 32P-postlabelling assay, which utilized one dimensional TLC chromatography and a subsequent HPLC analysis with UV and radioactivity detectors. In vitro with Ct-DNA the formation of N7-dGMP and N 6-dAMP adducts were linear at a concentration range of 44 to 870 nmol of BMO per mg DNA at physiological pH. N7- dGMP and N 6-dAMP adducts were formed in a ratio of 200:1. In dGMP and in dAMP 48 % and 86 % of adducts were covalently bound to the C-2 carbon of BMO. CD-1 mice were inhalation exposed to butadiene for 5 days and 6 h per day. The N7-dGMP adduct level in lung samples of animals exposed to 200, 500 and 1300 ppm was 2.8 +/- 0.9 fmol, 11 +/- 2.0 fmol and 30 +/- 6.7 fmol in 10 mug DNA, respectively. The level of N 6-dAMP adducts in lung samples after 500 ppm and 1300 ppm exposure was 0.09 +/- 0.06 fmol and 0.11 +/- 0.05 fmol in 10 mug DNA. At 200 ppm the adduct level was below the detection limit. A sub-group of animals exposed to 1300 ppm was killed 3 weeks after the last exposure. N7-dGMP adducts were not detected but the level of N 6-dAMP adducts was not affected. N7-dGMP adducts were formed in a clear stereospecific manner in vivo. S -BMO adducts were the main product and represented 77 % (n = 4, SD = 2%) of total BMO adducts. No clear conclusion can be drawn about the enantiospecific DNA binding at the N 6 position of dAMP, because of the poor separation of the enantiomers. However, we could separate regioisomeric adducts which indicated that C-2 adducts represented 69 +/- 3 % of the total N 6 adducts formed in mice lung DNA. This observation is supported by the data derived from in vitro DNA experiments but is different to our previously published data, which indicates the 2:1 (C-1:C-2) ratio in regioisomer formation in nucleotides or nucleosides. We suggest that the data presented in this communication indicate a different mechanism between nucleotides and DNA in BMO-derived adduct formation- Dimroth rearrangement dominates in nucleotides, but in double stranded DNA a direct alkylation is probably the major mechanism of adduct formation.     

The formation of heart DNA adducts in F344 rat following dietary administration of heterocyclic amines

Most heterocyclic amines formed during the cooking of meat and fish have been shown to form adducts in the livers of rats. Recently, however, 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP), administered in the diet to Fischer 344 (F344) rats for 4 weeks, was shown to produce the highest levels of adducts in the heart. In the present study 2-amino-3-methylimidazo[4,5-f]quinoline (IQ), 2-amino-3,8-dimethylimidazo [4,5-f]quinoxaline (MeIQx), 3-amino-1,4-dimethyl-5H-pyrido[4,3-b]indole (Trp-P-1) and 2-amino-6-methyldipyrido[1,2-a:1',2'-d]imidazole (Glu-P-1) were given to F344 rats at carcinogenic dose levels (IQ 0.03%, MeIQx 0.04%, Trp-P-1 0.015%, Glu-P-1 0.05%) in the diet for 4 weeks. DNA adducts in the liver and heart were analyzed by 32P-postlabeling. DNA adducts were demonstrated to appear in the hearts of all animals exposed to heterocyclic amines at the following levels: IQ, 1.8 adducts/10(7) nucleotides, MeIQx, 3.8/10(7) ntd, Trp-P-1, 20/10(7) ntd and Glu-P-1, 7.2/10(7) ntd. Values for the heart were 10-20% of the respective liver adduct levels. Heart adducts increased linearly throughout the observed period when MeIQx was administered for up to 40 weeks. When MeIQx feeding was discontinued after 20 weeks and the animals subsequently given the basal diet, the adduct level at 20 weeks did not change during the following 20 weeks. A possible role for heart DNA alterations caused by food-borne heterocyclic amines in the development of age-related myopathies and cardiovascular disease is not inconceivable.     

Quantification of aristolochic acid-derived DNA adducts in rat kidney and liver by using liquid chromatography-electrospray ionization mass spectrometry

Aristolochic acid (AA), derived from the herbal genus Aristolochia and Asarum, has recently been shown to be associated with the development of nephropathy. Upon enzyme activation, AA is metabolized to the aristolactam-nitrenium ion intermediate, which reacts with the exocyclic amino group of the DNA bases via an electrophilic attack at its C7 position, leading to the formation of the corresponding DNA adducts. The AA-DNA adducts are believed to be associated with the nephrotoxic and carcinogenic effects of AA. In this study, liquid chromatography coupled with electrospray ionization mass spectrometry (LC-MS) was used to identify and quantify the AA-DNA adducts isolated from the kidney and liver tissues of the AA-dosed rats. The deoxycytidine adduct of AA (dC-AA) and the deoxyadenosine-AA adduct (dA-AA) were detected and quantified in the tissues of rats with one single oral dose (5mg or 30mg AA/kg body weight). The deoxyguanosine adduct (dG-AA), however, was detected only in the kidney of rats that were dosed at 30mg AA/kg body weight for three consecutive days. The amount of AA-DNA adducts found in the rats correlated well with the dosage.     

32P-analysis of DNA adducts in somatic and reproductive tissues of rats treated with the anticancer antibiotic, mitomycin C

Mitomycin C (MMC) is a clinically used drug with mutagenic and antitumor activities, presumably elicited through its covalent binding to DNA, however, little is known about MMC binding to DNA in vivo. A 32P-postlabeling method that does not require radiolabeled test compounds was employed here to study the formation of DNA adducts in somatic and reproductive tissues of rats 24 h after an i.p. dose of 9 mg/kg MMC. Among 14 tissues studied in female rats, MMC-DNA adduct levels were within a 2-fold range in 11 tissues, i.e. bladder, colon, esophagus, heart, kidney, liver, lung, ovary, pancreas, small intestine and stomach (minimum levels of 9.6-21.9 adducts per 10(7) N). Three other tissues, i.e. brain, spleen and thymus, exhibited lower adduct levels (0.2 5.4 and 1.4 adducts, respectively, per 10(7) N). Liver DNA adduct levels were 32% lower in male than in female rats. Testicular DNA contained 2.5 adducts per 10(7) N, i.e. 5.3 times less than ovarian DNA. 32P-labeled adduct patterns were qualitatively similar among the different tissues and consisted of 10 adducts, one of which comprised 71 (+/- 5)% of the total. All these adducts were chromatographically identical to adducts formed by the reaction of chemically reduced MMC with DNA in vitro, demonstrating that metabolic activation of MMC occurred via reduction. Using homopolydeoxyribonucleotides modified with MMC, in vivo adducts were shown to be mostly (greater than 90%) guanine derivatives and small amounts of adenine, cytosine and thymine products. Most of the adducts appeared to be monofunctional derivatives of DNA nucleotides. Dose-dependent MMC-DNA adduct formation was determined in rat liver over an 82-fold range of MMC administered (0.11-9.0 mg/kg). The lowest dose level studied was 4.5 times lower than the recommended single dose for human cancer chemotherapy (20 mg/m2). Thus, these results predict that 32P-postlabeling methodology is suitable to monitor and quantify DNA adducts in tissue biopsies of patients receiving MMC chemotherapy.     

32P-postlabelling detection of aromatic DNA adducts in peripheral blood lymphocytes from aluminium production plant workers

Aluminium production plant workers are exposed to a great number of airborne polycyclic aromatic hydrocarbons and epidemiological studies suggest that these workers are at increased risk of lung and bladder cancer. Blood samples from 46 workers at 2 primary aluminium plants and from 29 occupationally unexposed control individuals were analysed. DNA was isolated from the peripheral blood lymphocytes and aromatic DNA adducts were detected by 32P-postlabelling assay using the nuclease P1 digestion procedure for the enrichment of the adducts. The total levels of DNA adducts of exposed individuals varied from the detection limit of about 0.5 adducts/10(8) nucleotides up to 7.1 adducts/10(8) nucleotides and control adduct levels were up to 2.42 adducts/10(8) nucleotides. There was no significant difference between the mean adduct levels of the control group and of the individuals of one plant. However, the mean DNA adduct level obtained from workers of the second plant was significantly higher than that of the controls (p less than 0.001) and of the first plant (p less than 0.01), respectively. This difference can be attributed to differences in the design of technology and different levels of exposure at the 2 plants. The results of this study encourage further investigations of the use of peripheral white blood cells as marker cells and of 32P-postlabelling analysis for monitoring occupational exposure to mixtures of environmental carcinogenic pollutants.