Mutagenic activity and quantification of nitroarenes in surface soil in the Kinki region of Japan.
To clarify the mutagenic potential of surface soil in the Kinki region of Japan, particularly in Osaka and neighboring cities, 62 surface soil samples were collected and their organic extracts were examined by the Ames/Salmonella assay. All of the samples were mutagenic toward TA98 in both the presence and absence of a mammalian metabolic activation system (S9 mix). While all of the samples showed mutagenicity toward TA100 with S9 mix, only 45/62 (73%) were mutagenic without S9 mix. Fifty (81%) of the samples showed higher activity toward TA98 than TA100. The mean values of the mutagenicities of soil samples collected in Osaka prefecture (n=35) toward TA98 with and without S9 mix were 2315 and 1630 revertants per gram of soil, respectively, and these were 2.9 and 2.6 times as high as the values for samples from other prefectures (n=27), respectively. Three dinitropyrene (DNP) isomers, i.e. 1,3-, 1,6- and 1,8-DNP, and 3-nitrobenzanthrone (NBA) in the surface soil samples were quantified by fluorometric detection of the corresponding amino compounds, i.e. diaminopyrene isomers and 3-aminobenzanthrone, using high-performance liquid chromatography (HPLC). The three DNP isomers were detected in all of the soil samples (n=26) that were mainly collected in Osaka prefecture, and the amounts of 1,3-, 1,6- and 1,8-DNP were 6-1526, 11-1772 and 10-2092pg/g of soil, respectively. The contribution ratios of 1,3-, 1,6- and 1,8-DNP to the mutagenicity of soil extracts toward TA98 without S9 mix were 0.2-12, 0.3-12 and 0.5-27%, respectively. The amount of 3-NBA in soil samples (n=8) was 144-1158pg/g of soil, and the contribution ratio of 3-NBA to the mutagenicity of soil extracts was 2-38%. These results suggest that the surface soils in the Kinki region were highly polluted with mutagens and the pollution levels in Osaka prefecture were higher than those in other areas. DNP isomers and 3-NBA may be major mutagens that contaminate surface soil in this region.
Watanabe
Tetsushi
T
Department of Public Health, Kyoto Pharmaceutical University, Japan. watanabe@mb.kyoto-phu.ac.jp
Hasei
Tomohiro
T
Takahashi
Yoshifumi
Y
Otake
Shuhei
S
Murahashi
Tsuyoshi
T
Takamura
Takeji
T
Hirayama
Teruhisa
T
Wakabayashi
Keiji
K
D000818:Animals; D001551:Benz(a)Anthracenes / Q000032:analysis / Q000633:toxicity; D002851:Chromatography, High Pressure Liquid; D004784:Environmental Monitoring; D007564:Japan; D008297:Male; D009153:Mutagens / Q000032:analysis* / Q000633:toxicity*; D011721:Pyrenes / Q000032:analysis* / Q000633:toxicity*; D051381:Rats; D017207:Rats, Sprague-Dawley; D000091243:Ribosomal Protein S9; D012269:Ribosomal Proteins / Q000378:metabolism; D012486:Salmonella typhimurium / Q000187:drug effects / Q000235:genetics / Q000378:metabolism; D012987:Soil / Q000032:analysis*; D012989:Soil Pollutants / Q000032:analysis* / Q000633:toxicity*
D001551:Benz(a)Anthracenes; D009153:Mutagens; D011721:Pyrenes; D000091243:Ribosomal Protein S9; D012269:Ribosomal Proteins; D012987:Soil; D012989:Soil Pollutants; C033310:1,8-dinitropyrene; C033309:1,6-dinitropyrene; C037413:1,3-dinitropyrene; C117220:3-nitrobenzanthrone