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Polycyclic aromatic hydrocarbons (PAHs), nitrated PAHs and oxygenated PAHs in ambient air of the Marseilles area (South of France): Concentrations and sources

机译:马赛地区(法国南部)的环境空气中的多环芳烃(PAH),硝化PAH和含氧PAH:浓度和来源

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Ambient measurements (gas+particle phases) of 15 polycyclic aromatic hydrocarbons (PAHs), 17 nitrated PAHs (NPAHs) and 9 oxygenated PAHs (OPAHs) were carried out during July 2004 on three different sites (urban, sub-urban and rural) in the region of Marseilles (South of France). Atmospheric concentrations of these classes of polyaromatics are great of interest because of their high potential mutagenicity and carcinogenicity. OPAH concentrations were of the same order of magnitude as those of PAHs while NPAH concentrations were one to two orders lower. 9-Fluorenone and 9,10-anthraquinone were the most abundant OPAHs, accounting for about 60% and 20% of the total OPAH concentration. Respectively 1-and 2-nitronaphthalene were the most abundant NPAHs and were accounting for about 30-50% and 15-30% of the total NPAH concentration. NPAHs and OPAHs concentration levels were consistent with the characteristics of the sampling sites. Study of source specific ratios (2-nitrofluoranthene/1-nitropyrene) clearly showed those primary NPAH sources influence the urban and sub-urban sites whereas production of secondary NPAHs by gas phase reactions was prevalent at the rural site. The study of NPAH and OPAH sources suggested that gasoline engines were an important source of such compounds Whereas the dominant source of 1-nitropyrene, 2-nitrofluorene, 6-nitrochrysene and benz[a]anthracene-7,12-dione seems to be diesel vehicles. Finally, 9,10-anthraquinone presents a double origin: primary diesel emission and photochemical processes. Formation of 9,10-anthraquinone from anthracene ozonation was shown at the rural site. Further investigations will be necessary in order to discriminate when (before or during the sampling) the OPAHs are formed.
机译:2004年7月,在美国的三个不同地点(城市,郊区和乡村)对15种多环芳烃(PAH),17种硝化PAH(NPAH)和9种氧化PAH(OPAH)进行了环境测量。马赛地区(法国南部)。这些类别的多环芳烃的大气浓度非常令人感兴趣,因为它们具有很高的潜在诱变性和致癌性。 OPAH的浓度与PAH的数量级相同,而NPAH的浓度低1-2个数量级。 9-氟酮和9,10-蒽醌是最丰富的OPAH,分别占总OPAH浓度的60%和20%。 1-和2-硝基萘分别是最丰富的NPAH,分别占总NPAH浓度的30-50%和15-30%。 NPAHs和OPAHs的浓度水平与采样点的特征一致。对源特定比例(2-硝基荧蒽/ 1-硝基py)的研究清楚地表明,主要的NPAH来源影响城市和郊区,而通过气相反应生产次要的NPAH在农村地区很普遍。 NPAH和OPAH来源的研究表明,汽油发动机是此类化合物的重要来源,而1-硝基py,2-硝基芴,6-硝基丙烯和苯并[a]蒽-7,12-二酮的主要来源似乎是柴油。汽车。最后,9,10-蒽醌具有双重来源:一次柴油排放和光化学过程。在农村现场显示出蒽臭氧化反应生成9,10-蒽醌。为了区分何时(在采样之前或采样期间)OPAH,有必要进行进一步调查。

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