Journal
INTERNATIONAL ARCHIVES OF OCCUPATIONAL AND ENVIRONMENTAL HEALTH
Volume 95, Issue 6, Pages 1369-1388Publisher
SPRINGER
DOI: 10.1007/s00420-022-01843-x
Keywords
Underground mine; Occupational diesel exposure; PAHs; Biomarkers; Emission factors; Aftertreatment systems; Aerosols
Categories
Funding
- AFA Insurance [160323]
- Swedish Research Council FORTE [2018-00178]
- Forte [2018-00178] Funding Source: Forte
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This study investigated the effects of diesel exhaust and the use of renewable fuels on underground iron ore miners' personal exposure. The findings showed that the miners' exposures to carbon elemental and nitrogen dioxide were lower, possibly due to intensified emission legislation and new technologies. However, the exposure to semi-volatile polycyclic aromatic hydrocarbons was not affected, and ambient air sampling was not a reliable predictor of personal airborne exposure to these compounds.
Purpose Underground diesel exhaust exposure is an occupational health risk. It is not known how recent intensified emission legislation and use of renewable fuels have reduced or altered occupational exposures. We characterized these effects on multipollutant personal exposure to diesel exhaust and underground ambient air concentrations in an underground iron ore mine. Methods Full-shift personal sampling (12 workers) of elemental carbon (EC), nitrogen dioxide (NO2), polycyclic aromatic hydrocarbons (PAHs), and equivalent black carbon (eBC) was performed. The study used and validated eBC as an online proxy for occupational exposure to EC. Ambient air sampling of these pollutants and particle number size distribution and concentration were performed in the vicinity of the workers. Urine samples (27 workers) were collected after 8 h exposure and analyzed for PAH metabolites and effect biomarkers (8-oxodG for DNA oxidative damage, 4-HNE-MA for lipid peroxidation, 3-HPMA for acrolein). Results The personal exposures (geometric mean; GM) of the participating miners were 7 mu g EC m(-3) and 153 mu g NO2 m(-3), which are below the EU occupational exposure limits. However, exposures up to 94 mu g EC m(-3) and 1200 mu g NO2 m(-3) were observed. There was a tendency that the operators of vehicles complying with sharpened emission legislation had lower exposure of EC. eBC and NO2 correlated with EC, R = 0.94 and R = 0.66, respectively. No correlation was found between EC and the sum of 16 priority PAHs (GM 1790 ng m(-3)). Ratios between personal exposures and ambient concentrations were similar and close to 1 for EC and NO2, but significantly higher for PAHs. Semi-volatile PAHs may not be effectively reduced by the aftertreatment systems, and ambient area sampling did not predict the personal airborne PAHs exposure well, neither did the slightly elevated concentration of urinary PAH metabolites correlate with airborne PAH exposure. Conclusion Miners' exposures to EC and NO2 were lower than those in older studies indicating the effect of sharpened emission legislation and new technologies. Using modern vehicles with diesel particulate filter (DPF) may have contributed to the lower ambient underground PM concentration and exposures. The semi-volatile behavior of the PAHs might have led to inefficient removal in the engines aftertreatment systems and delayed removal by the workplace ventilation system due to partitioning to indoor surfaces. The results indicate that secondary emissions can be an important source of gaseous PAH exposure in the mine.
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