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Large PAHs detected in fine particulate matter emitted from light-duty gasoline vehicles

机译:在轻型汽油车排放的细颗粒物中检测到大量PAH

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摘要

Emission factors of large PAHs with 6-8 aromatic rings with molecular weights (MW) of 300-374 were measured from 16 light-duty gasoline-powered vehicles (LDGV) and one heavy-duty diesel-powered vehicle (HDDV) operated under realistic driving conditions. LDGVs emitted PAH isomers of MW 302, 326, 350, and 374, while the HDDV did not emit these compounds. This suggests that large PAHs may be useful tracers for the source apportionment of gasoline-powered motor vehicle exhaust in the atmosphere. Emission rates of MW 302, 326, and 350 isomers from LDGVs equipped with three-way catalysts (TWCs) ranged from 2 to 10 (μg L~(-1) fuel burned), while emissions from LDGVs classified as low emission vehicles (LEVs) were almost a factor of 10 lower. MW 374 PAH isomers were not quantified due to the lack of a quantification-grade standard. The reduced emissions associated with the LEVs are likely attributable to improved vapor recovery during the "cold-start" phase of the Federal Test Procedure (FTP) driving cycle before the catalyst reaches operating temperature. Approximately 2 (μgg~(-1) PM) of MW 326 and 350 PAH isomer groups were found in the National Institute of Standards and Technology standard reference material (SRM)#1649 (Urban Dust). The pattern of the MW 302, 326, and 350 isomers detected in SRM#1649 qualitatively matched the ratio of these compounds detected in the exhaust of TWC LDGVs suggesting that each gram of Urban Dust SRM contained 5-10 mg of PM originally emitted from gasoline-powered motor vehicles. Large PAHs made up 24% of the total LEV PAH emissions and 39% of the TWC PAH emissions released from gasoline-powered motor vehicles. Recent studies have shown certain large PAH isomers have greater toxicity than benzo[a]pyrene. Even though the specific toxicity measurements on PAHs with MW > 302 have yet to be performed, the detection of significant amounts of MW 326 and 350 PAHs in motor vehicle exhaust in the current study suggests that these compounds may pose a significant public health risk.
机译:从16辆轻型汽油动力汽车(LDGV)和1辆重型柴油动力汽车(HDDV)实际测量了具有6-8个芳环的分子量(MW)为300-374的大型PAHs的排放因子驾驶条件。 LDGV排放出MW 302、326、350和374的PAH异构体,而HDDV则不排放这些化合物。这表明,大的PAHs可能是有用的示踪剂,用于大气中以汽油为动力的机动车尾气的来源分配。配备三效催化剂(TWC)的LDGV的MW 302、326和350异构体的排放速率范围为2至10(燃烧的微克L〜(-1)燃料),而归类为低排放车辆(LEV)的LDGV的排放速率)几乎降低了10倍。 MW 374 PAH异构体由于缺乏定量级标准而无法定量。与LEV相关的排放减少可能归因于在催化剂达到工作温度之前的联邦测试程序(FTP)驾驶循环的“冷启动”阶段中蒸汽回收率的提高。在美国国家标准技术研究院标准参考材料(SRM)#1649(城市粉尘)中发现了MW 326和350 PAH异构体的大约2个(μgg〜(-1)PM)。在SRM#1649中检测到的MW 302、326和350异构体的模式与TWC LDGV排气中检测到的这些化合物的比率定性匹配,这表明每克城市粉尘SRM包含5-10 mg最初从汽油中排放的PM动力的汽车。大型PAH占LEV PAH排放总量的24%和TWC PAH排放的39%(由汽油驱动的机动车辆排放)。最近的研究表明,某些大的PAH异构体比苯并[a] re具有更大的毒性。尽管尚未对MW> 302的PAHs进行特定的毒性测量,但在本研究中检测到机动车尾气中有大量MW 326和350 PAHs,这表明这些化合物可能构成重大的公共健康风险。

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