Prevedouros Konstantinos, Jones Kevin C, Sweetman Andrew J
Department of Environmental Science, Institute of Environmental and Natural Sciences, Lancaster University, Lancaster LA1 4YQ, UK.
Chemosphere. 2004 Jul;56(3):195-208. doi: 10.1016/j.chemosphere.2004.02.032.
This paper presents the results from an exercise in atmospheric contaminant fate modelling, which had three main objectives: (1) to investigate the balance between estimated national atmospheric emissions of six selected PAHs and observed ambient measurements for the UK, as a means of testing the current emission estimates; (2) to investigate the potential influence of seasonally dependent environmental fate processes on the observed seasonality of air concentrations; and (3) after undertaking the first two objectives, to make inferences about the likely magnitude of seasonal differences in sources. When addressing objective 1 with annually averaged emissions data, it appeared that the UK PAH atmospheric emissions inventory was reasonably reliable for fluorene, fluoranthene, pyrene, benzo[a]pyrene and benzo[ghi]perylene--but not so for phenanthrene. However, more detailed analysis of the seasonality in environmental processes which may influence ambient levels, showed that the directions and/or magnitudes of the predicted seasonality did not coincide with field observations. This indicates either that our understanding of the environmental fate and behaviour of PAHs is still limited, and/or that there are uncertainties in the emissions inventories. It is suggested that better quantification of PAH sources is needed. For 3- and 4-ringed compounds, this should focus on those sources which increase with temperature, such as volatilisation from soil, water, vegetation and urban surfaces, and possible microbially-mediated formation mechanisms. The study also suggests that the contributions of inefficient, diffusive combustion processes (e.g. domestic coal/wood burning) may be underestimated as a source of the toxicologically significant higher molecular weight species in the winter. It is concluded that many signatory countries to the UNECE POPs protocol (which requires them to reduce national PAH emissions to 1990 levels) will experience difficulties in demonstrating compliance, because source inventories for 1990 and contemporary situations are clearly subject to major uncertainties.
本文介绍了一项大气污染物归宿模型研究的结果,该研究有三个主要目标:(1)调查英国六种选定多环芳烃的国家大气排放估计值与观测到的环境测量值之间的平衡,以此作为检验当前排放估计值的一种方法;(2)研究季节性依赖的环境归宿过程对观测到的空气浓度季节性的潜在影响;(3)在前两个目标完成后,推断源中季节性差异的可能大小。在用年度平均排放数据处理目标1时,英国多环芳烃大气排放清单对于芴、荧蒽、芘、苯并[a]芘和苯并[ghi]苝似乎相当可靠,但对于菲则不然。然而,对可能影响环境水平的环境过程季节性进行更详细的分析表明,预测的季节性方向和/或幅度与实地观测结果不一致。这表明要么我们对多环芳烃的环境归宿和行为的理解仍然有限,要么排放清单存在不确定性。建议需要更好地量化多环芳烃的来源。对于三环和四环化合物,这应侧重于那些随温度增加的来源,如土壤、水、植被和城市表面的挥发,以及可能的微生物介导形成机制。该研究还表明,低效、扩散燃烧过程(如家庭燃煤/木材燃烧)作为冬季具有毒理学意义的高分子量物种的来源,其贡献可能被低估。得出的结论是,许多联合国欧洲经济委员会持久性有机污染物议定书的签署国(该议定书要求它们将国家多环芳烃排放量降至1990年水平)在证明合规方面将面临困难,因为1990年和当前情况的源清单显然存在重大不确定性。