Abstract
Abstract. Polycyclic aromatic hydrocarbons (PAHs) were analysed in bulk atmospheric deposition samples collected at four European high-mountain areas, Gossenköllesee (Tyrolean Alps), Redon (Central Pyrenees), Skalnate Pleso (High Tatra Mountains), and Lochnagar (Grampian Mountains) between 2004 and 2006. Sample collection was performed monthly in the first three sites and biweekly in Lochnagar. The number of sites, period of study and sampling frequency provide the most comprehensive description of PAH fallout in high mountain areas addressed so far. The average PAH deposition fluxes in Gossenköllesee, Redon and Lochnagar ranged between 0.8 and 2.1 µg m−2 month−1, and in Skalnate Pleso it was 9.7 µg m−2 month−1, showing the influence of substantial inputs from regional emission sources. The deposited distributions of PAHs were dominated by parent phenanthrene, fluoranthene and pyrene, representing 32 %–60 % of the total. The proportion of phenanthrene, the most abundant compound, was higher at the sites of lower temperature, Gossenköllesee and Skalnate Pleso, showing higher transfer from gas phase to particles of the more volatile PAHs. The sites with lower insolation, e.g. those located at lower altitude, were those with a higher proportion of photooxidable compounds such as benz[a]anthracene. According to the data analysed, precipitation is the main driver of PAH fallout. However, when rain and snow deposition were low, particle settling also constituted an efficient driver for PAH deposition. Redon and Lochnagar were the two sites receiving the highest amounts of rain and snow and the fallout of PAH fluxes was related to this precipitation. No significant association was observed between long-range backward air trajectories and PAH deposition in Lochnagar, but in Redon PAH fallout at higher precipitation was essentially related to air masses originating from the North Atlantic, which were dominant between November and May (cold season). In these cases, particle-normalised PAH fallout was also associated with higher precipitation as these air masses were concurrent with lower temperatures, which enhanced gas to particle partitioning transfer. In the warm season (June–October), most of the air masses arriving at Redon originated from the south and particle deposition was enhanced as consequence of Saharan inputs. In these cases, particle settling was also a driver of PAH deposition despite the low overall PAH content of the Saharan particles. In Gossenköllesee, the site receiving lowest precipitation, PAH fallout was also related to particle deposition. The particle-normalised PAH fluxes were significantly negatively correlated to temperature, e.g. for air masses originating from central and eastern Europe, showing a dominant transfer from gas phase to particles at lower temperatures, which enhanced PAH fallout, mainly of the most volatile hydrocarbons. Comparison of PAH atmospheric deposition and lacustrine sedimentary fluxes showed much higher values in the latter case of 24–100 µg m−2 yr−1 vs. 120–3000 µg m−2 yr−1. A strong significant correlation was observed between these two fluxes, which is consistent with a dominant origin related to atmospheric deposition at each site.
Highlights
Polycyclic aromatic hydrocarbons (PAHs) are semi-volatile organic compounds (SOCs) originating from incomplete combustion and pyrolysis of carbonaceous materials
A strong contrast is found between the total PAH mean fluxes found in Lochnagar, Gossenköllesse and Redon of 0.80–2.1 μg m−2 month−1, and in Skalnate Pleso of 9.7 μg m−2 month−1, the latter showing PAH deposition fluxes between 5 and 10 times higher than the others
The PAH and benzo[a]pyrene deposition fluxes recorded in the studied high mountain areas of Europe (790– 2413 m) range among the lowest described in remote, rural, coastal, suburban, urban or industrial areas
Summary
Polycyclic aromatic hydrocarbons (PAHs) are semi-volatile organic compounds (SOCs) originating from incomplete combustion and pyrolysis of carbonaceous materials. In addition to natural sources, the global emissions of these compounds are dominated by anthropogenic activity such as fossil fuel combustion (Wild and Jones, 1995; Pacyna et al, 2003), which are responsible for their ubiquitous occurrence in the environment, especially in urban/industrial regions. In Europe, the emission of PAHs in 2004 was estimated about 5.1×104 tons (calculated for 16 PAHs), with residential combustion representing 88 % of the total contribution, followed by industrial activities (van der Gong et al, 2007). Implementation of regulatory activity caused an initial decrease in PAH emissions (Meijer et al, 2008) but recent studies showed that PAHs have increased globally as a consequence of a higher urban population, energy consumption and vehicle use (van Metre and Mahler, 2005)
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