Genotoxicity of coke-oven and urban air particulate matter in in vitro acellular assays coupled with 32P-postlabeling and HPLC analysis of DNA adducts.

This study is an in vitro part of the ongoing biomarker studies with population from a polluted region of Northern Bohemia and coke-oven workers from Czech and Slovak Republics. The aim of this study is to compare DNA adduct forming ability of chemical compound classes from both the urban and coke-oven extractable organic mass (EOM) of airborne particles. The crude extracts were fractionated into seven fractions by acid-base partitioning and silica gel column chromatography. In in vitro acellular assays we used calf thymus DNA (CT DNA) with oxidative (+S9) and reductive activation mediated by xanthine oxidase (+XO) under anaerobic conditions. Both the butanol and nuclease P1 versions of 32P-postlabeling for detection of bulky aromatic and/or hydrophobic adducts were used. The results showed that the spectra of major DNA adducts resulting from both the in vitro assays are within the fractions similar for both the urban and coke-oven samples. The highest DNA adduct levels with S9-activation were detected for the neutral aromatic fraction, followed by slightly polar and acidic fractions for both samples. With XO-mediated metabolism, the highest DNA adduct levels were detected for both the acidic fractions. Assuming additivity of compound activities, then the acidic fraction, which in the urban sample comprises a major portion of EOM mass (28%), may contain the greatest activity in both in vitro assays (39 and 69%, +S9 and +XO, respectively). In contrast, the aromatic fraction constituting only 8% of total urban EOM mass may account for comparable activity (34%) with organic acids. The highest DNA adduct forming activity of the coke-oven sample accounts for the aromatic fraction (82 and 63%, +S9 and +XO, respectively) that also contains the greatest portion of the total EOM (48%). To characterize some of the specific DNA adducts formed, we coupled TLC on 20x20 cm plates with HPLC analysis of 32P-postlabeled adducts. In both S9-treated samples of the aromatic fraction, we tentatively identified DNA adducts presumably diolepoxide-derived from: 9-hydroxy-benzo[a]pyrene (9-OH-B[a]P), benzo[a]pyrene-r-7,t-8-dihydrodiol-t-9,10-epoxide[+/-] (anti-BPDE), benzo[b,j,k]fluoranthenes (B[b]F, B[j]F, B[k]F), chrysene (CHRY), benz[a]-anthracene (B[a]A) and indeno[cd]pyrene (I[cd]P). These DNA adducts accounted for about 57% of total DNA adducts detected in both S9-treated samples of the aromatic fraction. DNA adducts of XO-treated samples were sensitive to nuclease P1 and HPLC profiles of the major adducts were markedly different from the major adducts of S9-treated samples. However, the combination of TLC and HPLC did not confirm the presence of DNA adducts derived from 1-nitropyrene (1 NP), 9-nitroanthracene (9 NA) and 3-nitrofluoranthene (3 NF) that were detected by GC-MS in the slightly polar fraction. We concluded that the chemical fractionation procedure facilitates the assessing of DNA adduct forming ability of different chemical compound classes. However, based on the results obtained with the whole extracts, it does not fulfil a task of the actual contribution of individual fractions within the activity of the whole extracts. Our results are the first in detecting of DNA adducts derived from urban air and coke-oven particulate matter.