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Although it is known that sunlight is carcinogenic,few molecular data are available concerning the mutagenic effects of ultraviolet (UV) B (290-320 nm) and UVA (320-400 nm) radiation in human cells. To analyze the biologic effects of UVA and UVB, we irradiated the 293 human cell line, derived from adenovirus-transformed human embryonic kidney cells, in which we had stably introduced a shuttle vector harboring the lacZ' bacterial gene as the mutagenesis target. Identical cell survival occurred after UVA doses 700-fold higher than UVB. This comparable to the UVA/UVB ratio that reaches the basal cell layer of the skin after sunlight exposure with UVB sunscreen. The frequency of UVA- and UVB- induced mutations increased with the UV dose as cell survival decreased. At cell survival levels greater than 10%, UVA and UVB induced similar frequencies of mutations in the episomal lacZ gene, whereas for cell survival lower than 10%, UVA induced twice as many mutations as UVB. Sequence analysis of 81 independent lacZ mutants (36 UVA- and 45 UVB-induced) revealed specific characteristics for some UV-induced-mutations, particularly for UVB. Mutations at A/T base pairs were induced more frequently by UVA than by UVB. The UVA-induced mutation spectrum that we have observed in human cells may help help to elucidate the mechanism of skin carcinogenesis.

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Twenty-three polycyclic aromatic hydrocarbons (PAH) were determined in atmospheric particulate matter in 4 places of the Paris area at several times of the year. Fractionation was performed by reversed-phase high-pressure liquid chromatography. Determination was done by recording emission or excitation fluorescence spectra via a stopped-flow technique. Triphenylene was also extemporaneously determined by its phosphorescence spectrum at low temperature. Among the PAH determined dibenz(e,ghi)perylene has not been detected before in atmospheric particulate matter. The 10 more abundant PAH ranged from 0.1 to 40 ng/m3 of filtered air. Concentrations in August are from 14 to 250 times less than in January depending on the PAH. The reasons for this difference of behaviour among the PAH were investigated with regard to their photochemical and non-photochemical reactivity.

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