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M Hämeilä

Publications and source records attributed to M Hämeilä.

4 recordsLinked to original sources

Mutagenicity of bitumen and asphalt fumes.

The mutagenicity of asphalt fumes was tested with the Salmonella bioassays. The aim was to investigate if recycled additives modify the genotoxicity of emissions. Recycling of old asphalt is increasing, and we studied also the mutagenicity of emissions sampled during the re-use of asphalt. The composition of vapours and fumes were analysed by gas chromatography and by liquid chromatography. Bitumens containing coal fly ash (CFA) or waste plastics were heated to the paving temperatures in the laboratory. In the field, bitumen fumes were collected during paving of stone mastic asphalts (lime or CFA as a filler), remixing of stone mastic asphalt (lime or CFA as a filler), and of asphalt concrete. All the lab-generated vapour fractions were non-mutagenic. The particulate fractions were mutagenic with TA98 in the presence of the S9 activation. In addition, the lab-fumes from bitumen containing waste plastics were positive with both strains without S9. Only particulate fractions sampled in the field were tested. They were mutagenic with and without metabolic activation with both strains. The mutagenic potency of the field samples was higher than that of the lab-generated fumes without S9, and the remixing fumes were more mutagenic than the normal paving and lab-generated fumes with S9. The use of inorganic additive, CFA, did not change the mutagenicity of the fumes, whereas the organic additive, waste plastics, increased the mutagenicity of the laboratory emissions significantly.

Air Pollutants, Occupational↗

Genotoxic effects and chemical compositions of four creosotes.

Four creosotes used in Finland for impregnating wood were tested in the Ames Salmonella test, the SCE test and the SOS chromotest. Compounds volatile at 37 degrees C were assayed using the taped plate testing protocol. The creosotes were fractionated according to their natural boiling ranges and the fractions were tested in the Ames Salmonella assay. Chemical compositions of creosotes and fractions were determined by high resolution gas chromatography/mass spectrophotometry techniques and by reversed phase high performance liquid chromatography. Mutagenic activities were shown to reside in fractions having the highest boiling point ranges (greater than 290 degrees C). The concentrations of mutagenic polycyclic aromatic hydrocarbons in creosotes and in some of their corresponding distillation fractions, when compared with mutagenic activities, indicated synergistic or antagonistic interactions.

Animals↗

Exposure to creosote in the impregnation and handling of impregnated wood.

The major components of vapors and polycyclic aromatic hydrocarbons in particulate matter were identified and quantified in two creosote impregnation plants and in the handling of treated wood. The vapors were collected on XAD-2 resin (recovery in the range of 82-102%) and analyzed by gas chromatography. Particulate polycyclic aromatic hydrocarbons were collected on glass fiber filters and analyzed with high-pressure liquid chromatography with a fluorescence detector. The main components of the vapors were naphthalene, methyl naphthalenes, indene, phenol, and its methyl homologues, benzothiophene, diphenyl, acenaphthene and fluorene. The exposure of the workers to vapors varied between 0.1 and 11 mg/m3. The concentrations of particulate polycyclic aromatic hydrocarbons varied between 0.2 and 46 micrograms/m3. The benzo(a)pyrene concentration was under 0.03 micrograms/m3, except in manual metal-arc welding and in the boring of railroad ties, where it was 0.24-0.89 micrograms/m3. In the measurement of creosote vapors, naphthalene could be used as an indicator agent.

Air Pollutants, Occupational↗