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.

Urinary 1-naphthol excretion in the assessment of exposure to creosote in an impregnation facility.

OBJECTIVES: This study explored the possibility of using urinary 1-naphthol excretion as a marker of complex exposure among workers handling creosote. METHODS: Urine specimens of 6 workers from a creosote impregnation plant, where railroad ties were impreganted with coal tar creosote, were collected during 1 workweek, and the concentration of 1-naphthol was determined. 1-Naphthol in spot urine samples of 5 occupationally nonexposed male smokers was used as the background reference. Concurrently, naphthalene and 10 different polycyclic aromatic hydrocarbons (PAH) were determined in personal air samples. RESULTS: The mean airborne exposure of the workers was 1.5 mg/m3 for vaporous naphthalene, 5.9 micrograms/m3 for particulate PAH and 1.4 micrograms/m3 for PAH with 4-6 aromatic rings. The mean urinary concentration of 1-naphthol at the end of the workshift was 20.5 (range 3.5-62.1) mumol/l, whereas the referents' urinary concentration was below the detection limit (0.07 mumol/l). Airborne naphthalene correlated fairly well with 1-naphthol when measured at the end of the shift (r = 0.745). CONCLUSIONS: This method of analysis for 1-naphthol is sufficiently sensitive for measuring low occupational exposures to naphthalene. Low background exposures are, however, unlikely to result in detectable urinary levels of 1-naphthol. Since naphthalene is the most abundant compound in creosote vapor, urinary 1-naphthol determination serves well as a biological marker of exposure to vaporous creosote. Urinary 1-naphthol alone is not, however, a suitable marker for inhalatory or cutaneous exposure to PAH originating from creosote.

Cancer risk for European asphalt workers.

OBJECTIVES: The feasibility of a European epidemiologic study of cancer risk among asphalt workers was examined in Western Europe. The study was motivated by occupational and public health concern about possible health risk from exposure to bitumen fumes. METHODS: Information on the accessibility and quality of epidemiologic resources, retrospective worker records, mortality and cancer incidence records, and exposures was requested from research institutes and road paving and asphalt mixing companies in 15 European countries. RESULTS: Research institutes and asphalt companies in 12 countries responded. It was found that at least 44 companies in seven countries can be included in a retrospective mortality study of a minimum of 32,000 employees with 356,000 person-years (over 100 lung cancers). Coal tar will be an important confounder for these data. The power of a cohort study of workers who have never worked with tar-containing materials remains insufficient. Even in an ambispective study extending to the year 2005, the expected lung cancer deaths in a tar-free cohort would be only four. CONCLUSIONS: The results suggest that a case-referent study of lung cancer, nested in an international cohort of asphalt workers, represents the design of choice, conditionally on the possibility of assessing relevant individual life-time exposures. A cross-sectional determination of relevant biomarkers of exposure such as adducts in lymphocytes or the presence of metabolites of polycyclic aromatic compounds in urine in a group of workers exposed to bitumen fumes will provide further relevant information.

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.