||Hepatic Metabolism of the Environmental Mutagen 2-Nitrofluoranthene.
Ball, L. M. ;
Nishioka, M. G. ;
Lewtas, J. ;
||North Carolina Univ. at Chapel Hill. Dept. of Environmental Sciences and Engineering. ;Battelle Columbus Labs., OH.;Health Effects Research Lab., Research Triangle Park, NC. Genetic Bioassay Branch.
Air pollution ;
Exhaust gases ;
Aromatic polycyclic hydrocarbons ;
Environmental tests ;
Combustion products ;
||Most EPA libraries have a fiche copy filed under the call number shown. Check with individual libraries about paper copy.
||2-Nitrofluoranthene has recently been demonstrated to be the most abundant nitrated fluoranthene in organic extracts of ambient air particulate matter collected both in Philadelphia (Nishioka et al., unpublished results) and in Southern California. Whereas the better-known isomer 3-nitrofluoranthene (3-NFA) is found in combustion emissions such as diesel exhaust (2) and arises from direct nitration by NO2/N204 or the NO(+2), 2-NFA appears to be formed from fluoranthene in the ambient air by a specific atmospheric transformation mechanism, possibly initiated by addition of an OH radical at the site of highest electron density. An analogous pathway would lead to the formation of 2-nitropyrene which was observed in rural ambient air particulate matter in Denmark. Other nitrated polycyclic aromatic hydrocarbons (nitroPAH) present in the environment are known to be potent bacterial mutagens. Their genotoxicity in prokaryotes is largely due to generation of active electrophiles (leading to formation of covalenty-bound C8-deoxyguanosine DNA adducts) by nitroreduction.
||Prepared in cooperation with Battelle Columbus Labs., OH. Sponsored by Health Effects Research Lab., Research Triangle Park, NC. Genetic Bioassay Branch.
|PUB Date Free Form
||68A; 43F; 91A
||PC A03/MF A01