Composition and effects of inhalable size fractions of atmospheric aerosols in the polluted atmosphere: part I. PAHs, PCBs and OCPs and the matrix chemical composition

. 2014 May ; 21 (9) : 6188-204. [epub] 20140201

Jazyk angličtina Země Německo Médium print-electronic

Typ dokumentu časopisecké články, práce podpořená grantem

Perzistentní odkaz   https://www.medvik.cz/link/pmid24488522

Atmospheric particulate matter (PM) abundance, mass size distribution (MSD) and chemical composition are parameters relevant for human health effects. The MSD and phase state of semivolatile organic pollutants were determined at various polluted sites in addition to the PM composition and MSD. The distribution pattern of pollutants varied from side to side in correspondence to main particle sources and PM composition. Levels of particle-associated polycyclic aromatic hydrocarbons (PAHs) were 1-30 ng m(-3) (corresponding to 15-35 % of the total, i.e., gas and particulate phase concentrations), of polychlorinated biphenyls (PCBs) were 2-11 pg m(-3) (4-26 % of the total) and of DDT compounds were 2-12 pg m(-3) (4-23 % of the total). The PM associated amounts of other organochlorine pesticides were too low for quantification. The organics were preferentially found associated with particles <0.45 μm of aerodynamic equivalent diameter. The mass fractions associated with sub-micrometer particles (PM0.95) were 73-90 %, 34-71 % and 36-81 % for PAHs, PCBs and DDT compounds, respectively. The finest particles fraction had the highest aerosol surface concentration (6.3-29.7)×10(-6) cm(-1) (44-70 % of the surface concentration of all size fractions). The data set was used to test gas-particle partitioning models for semivolatile organics for the first time in terms of the organics' MSD and size-dependent PM composition. The results of this study prove that at the various sites particles with diverse size, matrix composition, amount of contaminants and toxicological effects occur. Legislative regulation based on gravimetric determination of PM mass can clearly be insufficient for assessment.

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Biomarkers. 2006 May-Jun;11(3):221-32 PubMed

Chem Soc Rev. 2013 Dec 21;42(24):9333-91 PubMed

J Environ Monit. 2011 Dec;13(12):3358-64 PubMed

Environ Sci Technol. 2009 Sep 1;43(17):6851-6 PubMed

Environ Sci Technol. 2005 Sep 1;39(17):6638-43 PubMed

Environ Sci Pollut Res Int. 2009 Jan;16(1):65-72 PubMed

Environ Sci Technol. 1983 Nov 1;17(11):673-9 PubMed

Chem Soc Rev. 2012 Oct 7;41(19):6606-30 PubMed

Part Fibre Toxicol. 2006 Aug 14;3:11 PubMed

Mutat Res. 2006 Nov-Dec;613(2-3):103-22 PubMed

Environ Sci Technol. 2001 Jan 1;35(1):1-9 PubMed

Environ Sci Technol. 2008 Aug 1;42(15):5541-7 PubMed

Toxicol Lett. 1998 Aug;96-97:253-61 PubMed

Environ Int. 2013 Apr;54:26-34 PubMed

Environ Sci Technol. 1984 May 1;18(5):375-82 PubMed

Environ Sci Pollut Res Int. 2005 Jul;12(4):213-20 PubMed

Environ Int. 2007 Aug;33(6):727-35 PubMed

Chemosphere. 2009 Jun;76(1):98-106 PubMed

Mutat Res. 2013 Jun 14;754(1-2):1-6 PubMed

Environ Sci Technol. 2004 Jul 15;38(14):3793-803 PubMed

Environ Int. 2014 Feb;63:64-70 PubMed

Environ Sci Pollut Res Int. 2005;12(1):10-20 PubMed

Environ Int. 2009 Oct;35(7):1066-71 PubMed

Sci Total Environ. 1997 Oct 20;205(2-3):137-44 PubMed

J Environ Monit. 2007 Jun;9(6):557-63 PubMed

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