Environmental pollution with nitroaromatic compounds may pose health hazards. We have examined the tumorigenicity in female Sprague-Dawley rats of 2,7-dinitrofluorene (2,7-diNF) and 9-oxo-2,7-diNF administered by intraperitoneal (i.p.) and oral routes at 10 lmol/kg body weight, 3 times per week for 4 weeks. After i.p. treatment, the estimated median latency for the combined malignant and benign mammary tumors was decreased in 2,7-diNF-(p 5 0.003) or 9-oxo-2,7-diNF-treated (p 5 0.007), relative to vehicle-treated rats (42 or 64 vs. 80 weeks, respectively), whereas after oral dosing, there were no significant differences. At 90 weeks, the malignant mammary tumor incidence in 2,7-diNF-, 9-oxo-2,7-diNF-and vehicle-i.p. treated rats was 44 (p 5 0.02 vs. vehicletreated), 25 and 6%, respectively. Liver and mammary gland DNA was analyzed by HPLC combined with electrospray tandem mass spectrometry for the presence of a deoxyguanosine (dG-2,7-diNF) adduct and a deoxyadenosine (dA-2,7-diNF) adduct derived from 2,7-diNF, and a deoxyguanosine (dG-9-oxo-2,7-diNF) adduct derived from 9-oxo-2,7-diNF. Both dG-2,7-diNF and dA-2,7-diNF were detected in DNA of 2,7-diNF-treated rats, whereas only very low levels of dG-9-oxo-2,7-diNF were detected in DNA of 9-oxo-2,7-diNF-treated rats. After i.p. treatment, the dA-2,7-diNF level was higher (p < 0.01) in the mammary gland than liver (13.6 vs. 7.8 adducts/10 8 nucleotides). In the mammary gland, the dG-2,7-diNF level was higher (p < 0.05) after i.p. than oral dosing and also higher (p < 0.05) than in the liver (36 vs. 8.6 and vs. 9.1 adducts/10 8 nucleotides, respectively). The preferential display of carcinogenicity and genotoxicity in the mammary gland by low doses of 2,7-diNF signifies its potential relevance for environmental breast cancer. ' 2008 Wiley-Liss, Inc.Key words: environmental nitroaromatic; rat; mammary cancer; genotoxicity Nitrated polycyclic aromatic hydrocarbons (nitro-PAHs) are widespread environmental pollutants resulting from the incomplete combustion of fossil fuels and atmospheric nitration. [1][2][3] Potential harmful effects of several nitro-PAHs are ascribed to their metabolic activation via nitroreduction to genotoxic species. 4,5 The risks associated with exposure of human populations to mutagenic and carcinogenic nitro-PAHs through inhalation, ingestion or dermal exposure are recognized. 3,[6][7][8][9][10] Nitrofluorenes and their C9-oxidized derivatives constitute a significant fraction of environmental nitro-PAHs. 3,6,7,11,12 2-Nitrofluorene (2-NF) is an abundant compound in diesel, gasoline and kerosene exhausts, and is present in urban air particles at especially high levels (310-5,220 pg/m 3 ) during winter, due to coal and kerosene heating. 6,12 The concentration of 2,7-dinitrofluorene (2,7-diNF; Fig. 1) in the air of Tokyo has been reported to be $30-and $10-fold greater than that of 2-NF and 1-nitropyrene, respectively. 6,13 Administration of 2,7-diNF, 2-NF and 2,5-diNF to female Sprague-Dawley rats at 1.62 mmol/kg of diet for 8 months yielded chi...