Literature DB >> 15180051

Phase and size distribution of polycyclic aromatic hydrocarbons in diesel and gasoline vehicle emissions.

B Zielinska1, J Sagebiel, W P Arnott, C F Rogers, K E Kelly, D A Wagner, J S Lighty, A F Sarofim, G Palmer.   

Abstract

Emission measurements were obtained for a variety of military vehicles at Hill Air Force Base (Ogden, UT) in November 2000 as part of a Strategic Environmental Research and Development Program. Aircraft ground support equipment vehicles using gasoline, diesel, and JP8 fuels were tested using chassis dynamometers under predetermined load. The exhaust from the tested vehicle was passed to a dilution tunnel where it was diluted 30-40 times and collected using Micro-Orifice Uniform Deposit Impactor (MOUDI) fitted with aluminum substrates, an XAD-coated annular denuder, and a filter followed by a solid adsorbent. All MOUDI substrates were analyzed for mass and for organic and elemental (EC) carbon by the thermal/optical reflectance method and for polycyclic aromatic hydrocarbons (PAHs) by GC/MS. Black carbon was measured with a photoacoustic instrument. The denuder and filter/solid adsorbent samples were analyzed for semivolatile PAH. Overall, there is more mass and higher EC contribution when the vehicle is run under higher load in comparison with the low load. However, older vehicles generally show more mass and EC emissions than newer vehicles, and there is a shift toward smaller particle sizes for the low load, which is most pronounced for newer vehicles. The particle-associated semivolatile PAHs and nonvolatile four-through six-ring PAHs are present predominantly on the submicron particles collected on MOUDI stages 0.1-0.18, 0.18-0.32, and 0.32-0.56 microm. For the low-load runs, the distribution of PAHs seems to be shifted toward smaller size particles. The gas-particle phase distribution of semivolatile PAHs depends also on the engine loading. For idle, not only are the more volatile two- and three-ring PAHs, from naphthalene to dimethylphenanthrenes, retained on the denuder portion, but also less volatile four-ring PAHs, such as fluoranthene and pyrene, are retained by the denuder at the 80-90% range, which implies that they are present predominantly in the gas phase. In contrast, for engines under high loads, a much larger portion of three- and four-ring PAHs are partitioned to the particle phase.

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Year:  2004        PMID: 15180051     DOI: 10.1021/es030518d

Source DB:  PubMed          Journal:  Environ Sci Technol        ISSN: 0013-936X            Impact factor:   9.028


  21 in total

1.  Seasonal variation of the particle size distribution of n-alkanes and polycyclic aromatic hydrocarbons (PAHs) in urban aerosol of Guangzhou, China.

Authors:  X L Tang; X H Bi; G Y Sheng; J H Tan; J M Fu
Journal:  Environ Monit Assess       Date:  2006-06       Impact factor: 2.513

2.  Recovery and reactivity of polycyclic aromatic hydrocarbons collected on selected sorbent tubes and analyzed by thermal desorption-gas chromatography/mass spectrometry.

Authors:  M Ariel Geer Wallace; Joachim D Pleil; Donald A Whitaker; Karen D Oliver
Journal:  J Chromatogr A       Date:  2019-05-16       Impact factor: 4.759

3.  Characteristics of nano-/ultrafine particle-bound PAHs in ambient air at an international airport.

Authors:  Chia-Hsiang Lai; Kuen-Yuan Chuang; Jin-Wei Chang
Journal:  Environ Sci Pollut Res Int       Date:  2012-07-22       Impact factor: 4.223

4.  An oxygenated metabolite of benzo[a]pyrene increases hepatic β-oxidation of fatty acids in chick embryos.

Authors:  Ola Westman; Maria Larsson; Nikolaos Venizelos; Henner Hollert; Magnus Engwall
Journal:  Environ Sci Pollut Res Int       Date:  2014-01-03       Impact factor: 4.223

5.  Prenatal exposure to airborne polycyclic aromatic hydrocarbons and childhood growth trajectories from age 5-14 years.

Authors:  Andrew G Rundle; Dympna Gallagher; Julie B Herbstman; Jeff Goldsmith; Darrell Holmes; Abeer Hassoun; Sharon Oberfield; Rachel L Miller; Howard Andrews; Elizabeth M Widen; Lori A Hoepner; Frederica Perera
Journal:  Environ Res       Date:  2019-07-19       Impact factor: 6.498

6.  Polycyclic aromatic hydrocarbons study and toxic equivalency factor (TEFs) in Tehran, Iran.

Authors:  F Halek; Gh Nabi; A Kavousi
Journal:  Environ Monit Assess       Date:  2007-11-07       Impact factor: 2.513

7.  Atmospheric polycyclic aromatic hydrocarbons (PAHs) in the urban air of Delhi during 2003.

Authors:  Homdutt Sharma; V K Jain; Zahid H Khan
Journal:  Environ Monit Assess       Date:  2007-12-28       Impact factor: 2.513

8.  Factors and Trends Affecting the Identification of a Reliable Biomarker for Diesel Exhaust Exposure.

Authors:  David A Morgott
Journal:  Crit Rev Environ Sci Technol       Date:  2014-08       Impact factor: 12.561

9.  Particle- and gas-phase PAHs toxicity equivalency quantity emitted by a non-road diesel engine with non-thermal plasma technology.

Authors:  Jianbing Gao; Chaochen Ma; Shikai Xing; Yajie Zhang; Jiangquan Liu; Hao Feng
Journal:  Environ Sci Pollut Res Int       Date:  2016-08-09       Impact factor: 4.223

10.  Polycyclic Aromatic Hydrocarbons and Polychlorinated Dibenzo-p-Dioxins/Dibenzofurans in Microliter Samples of Human Serum as Exposure Indicators.

Authors:  Xiaoyan Xia; Alesia Carroll-Haddad; Nicole Brown; Mark J Utell; Col Timothy M Mallon; Philip K Hopke
Journal:  J Occup Environ Med       Date:  2016-08       Impact factor: 2.162

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