Investigation on sampling artifacts of particle associated PAHs using ozone denuder systems

Kai LIU , Fengkui DUAN , Kebin HE , Yongliang MA , Yuan CHENG

Front. Environ. Sci. Eng. ›› 2014, Vol. 8 ›› Issue (2) : 284 -292.

PDF (321KB)
Front. Environ. Sci. Eng. ›› 2014, Vol. 8 ›› Issue (2) : 284 -292. DOI: 10.1007/s11783-013-0555-7
RESEARCH ARTICLE
RESEARCH ARTICLE

Investigation on sampling artifacts of particle associated PAHs using ozone denuder systems

Author information +
History +
PDF (321KB)

Abstract

Polycyclic aromatic hydrocarbons (PAHs) are complex organic compounds which are identified as significant carcinogenic to human health. PAHs (mainly in particle phase) are susceptible to atmospheric oxidant gases, especially ozone, nitrogen oxides (NOx), hydroxyl radical (OH), and could be degraded on filters during sampling process, leading to an underestimation of ambient PAH concentrations. The goal of this work was to investigate particle associated PAHs sampling artifacts caused by ozone in summer of Beijing. Comparative sampling systems were operated simultaneously during the whole campaign, one with activated carbon ozone denuder, the other being set as conventional sampling system. Activated carbon denuder was testified to be highly efficient to eliminate ozone from air stream. In general, nine particle-bound PAHs observed from conventional sampler were all lower than those from ozone denuder system. The total PAHs (particle phase) concentration was averagely underestimated by 35.9% in conventional sampling procedure. Benzo[a]pyrene (BaP) had the highest percentage of mass loss. Ambient temperature was founded to have influences on PAHs sampling artifacts. High temperature can increase loss of particle associated PAHs during sampling.

Keywords

particle associated polycyclic aromatic hydrocarbons (PAHs) / ozone / denuder / sampling artifacts

Cite this article

Download citation ▾
Kai LIU, Fengkui DUAN, Kebin HE, Yongliang MA, Yuan CHENG. Investigation on sampling artifacts of particle associated PAHs using ozone denuder systems. Front. Environ. Sci. Eng., 2014, 8(2): 284-292 DOI:10.1007/s11783-013-0555-7

登录浏览全文

4963

注册一个新账户 忘记密码

References

[1]

Baek S O, Field R A, Goldstone M E, Kirk P W, Lest J N, Perry R. A review of atmospheric polycyclic aromatic hydrocarbons: source, fate and behavior. Water, Air, and Soil Pollution, 1991, 60(3–4): 279–300

[2]

Harrison R M, Smith D J T, Luhana L. Source apportionment of atmospheric polycyclic aromatic hydrocarbons collected from an urban location in Birmingham, U.K. Environmental Science & Technology, 1996, 30(3): 825–832

[3]

Khalili N R, Scheff P A, Holsen T M. PAH source fingerprints for coke ovens, diesel and gasoline engines, highway tunnels, and wood combustion emissions. Atmospheric Environment, 1995, 29(4): 533–542

[4]

Xu S S, Liu W X, Tao S. Emission of polycyclic aromatic hydrocarbons in China. Environmental Science & Technology, 2006, 40(3): 702–708

[5]

Bourotte C, Fouti M C, Taniguchi S, Bicego M C, Lotufo P A. A wintertime study of PAHs in fine and coarse aerosols in So Paulo city, Brazil. Atmospheric Environment, 2005, 39(21): 3799–3811

[6]

Choi H, Jedrychowski W, Spengler J, Camann D E, Whyatt R M, Rauh V, Tsai W Y, Perera F P. International studies of prenatal exposure to polycyclic aromatic hydrocarbons and fetal growth. Environmental Health Perspectives, 2006, 114(11): 1744–1751

[7]

Mumford J L, He X Z, Chapman R S, Cao S R, Harris D B, Li X M, Xian Y L, Jiang W Z, Xu C W, Chuang J C. Lung cancer and indoor air pollution in Xuan Wei, China. Science, 1987, 235(4785): 217–220

[8]

Halsall C J, Coleman P J, Davis B J, Burnett V, Waterhouse K S, Harding-Jones P, Jones K C. Polycyclic aromatic hydrocarbons in U.K. urban air. Environmental Science & Technology, 1994, 28(13): 2380–2386

[9]

Gigliotti C L, Dachs J, Nelson E D, Brunciak P A, Eisenreich S J. Polycyclic aromatic hydrocarbons in the New Jersey coastal atmosphere. Environmental Science & Technology, 2000, 34(17): 3547–3554

[10]

Nielsen T, Ramdahl T, Bjoerseth A. The fate of airborne polycyclic organic matter. Environmental Health Perspectives, 1983, 47: 103–114

[11]

Allen J O, Dookeran N M, Taghizadeh K, Lafleur A L, Smith K A, Sarofim A F. Measurement of oxygenated polycyclic hydrocarbons associated with size-segregated urban aerosol. Environmental Science & Technology, 1997, 31(7): 2064–2070

[12]

van Vaeck L, Van Cauwenberghe K. Conversion of polycyclic aromatic hydrocarbons on diesel particulate matter upon exposure to ppm levels of ozone. Atmospheric Environment, 1984, 18(2): 323–328

[13]

Peters J, Seifert B. Losses of benzo[a]pyrene under the conditions of high volume sampling. Atmospheric Environment, 1980, 14(1): 117–119

[14]

Grosjean D, Fung K, Harrison J. Interactions of polycyclic aromatic hydrocarbons with atmospheric pollutants. Environmental Science & Technology, 1983, 17(11): 673–679

[15]

Coutant R W, Brown L, Chuang J C, Riggin R M, Lewis R G. Phase distribution and artifact formation in ambient air sampling for polynuclear aromatic hydrocarbons. Atmospheric Environment, 1988, 22(2): 403–409

[16]

Tsapakis M, Stephanou E G. Collection of gas and particle semi-volatile organic compounds: use of an oxidant denuder to minimize polycyclic aromatic hydrocarbons degradation during high-volume air sampling. Atmospheric Environment, 2003, 37(35): 4935–4944

[17]

Liu Y, Sklorz M, Schnelle-Kreis J, Orasche J, Ferge T, Kettrup A, Zimmermann R. Oxidant denuder sampling for analysis of polycyclic aromatic hydrocarbons and their oxygenated derivates in ambient aerosol: evaluation of sampling artefact. Chemosphere, 2006, 62(11): 1889–1898

[18]

Schauer C, Niessner R, Pochl U. Polycyclic aromatic hydrocarbons in urban air particulate matter: decadal and seasonal trends, chemical degradation, and sampling artifacts. Environmental Science & Technology, 2003, 37(13): 2861–2868

[19]

Pitts Jr, Paur J N, Zielinska B, Arey J, Winer A M, Ramdahl T, Mejia V. Factors influencing reactivity of polycyclic aromatic hydrocarbons adsorbed on filters and ambient POM with ozone. Chemosphere, 1986, 15: 675–685

[20]

Goriaux M, Jourdain B, Temime B, Besombes J L, Marchand N, Albinet A, Leoz-Garziandia E, Wortham H. Field comparison of particulate PAH measurements using a low-flow denuder device and conventional sampling systems. Environmental Science & Technology, 2006, 40(20): 6398–6404

[21]

Pitts J N Jr, Paur H R, Zielinska B, Arey J, Winer A M, Ramdahl T, Mejia V. Factors influencing reactivity of polycyclic aromatic hydrocarbons adsorbed on filters and ambient POM with ozone. Chemosphere, 1986, 15(6): 675–685

[22]

Lin W L, Xu X B, Ge B Z, Zhang X C. Characteristics of gaseous pollutants at Gucheng, a rural site southwest of Beijing. Journal of Geophysical Research, 2009, 114(D2): D00G14

[23]

He K B, Yang F M, Ma Y L, Zhang Q, Yao X H, Chan C K, Cadle S, Chan T, Mulawa P. The characteristics of PM2.5 in Beijing, China. Atmospheric Environment, 2001, 35(29): 4959–4970

[24]

Cheng Y, He K B, Duan F K, Zheng M, Ma Y L, Tan J H. Positive sampling artifact of carbonaceous aerosols and its influence on the thermal-optical split of OC/EC. Atmospheric Chemistry and Physics, 2009b, 9(18): 7243–7256

[25]

Liu S Z, Tao S, Liu WX, Dou H, Liu Y, Zhao JY, Little M G, Tian Z F, Wang J F, Wang L G, Gao Y. Seasonal and spatial occurrence and distribution of atmospheric polycyclic aromatic hydrocarbons (PAHs) in rural and urban areas of the North Chinese Plain. Environmental Pollution, 2008, 156(3): 651–656

[26]

Bidleman T F. Atmospheric processes-wet and dry deposition of organic compowzds are controlled by their vapor-particle partitioning. Environmental Science & Technology, 1988, 22(4): 361–367

[27]

Naumova Y Y, Offenberg J H, Eisenreich S J, Meng Q, Polidori A, Turpin B J, Weisel C P, Morandi M T, Colome S D, Stock T H, Winer A M, Alimokhtari S, Kwon J, Maberti S, Shendell D, Jones J, Farrar C. Gas/particle distribution of polycyclic aromatic hydrocarbons in coupled outdoor/indoor atmospheres. Atmospheric Environment, 2003, 37(5): 703–719

[28]

Lee J Y, Kim Y P, Kang C H. Temporal trend and long-range transport of particulate polycyclic aromatic hydrocarbons at Gosan in northeast Asia between 2001 and 2004. Journal of Geophysical Research-Part D, 2006, 111(D11): 11–18

[29]

Yunker M B, Macdonald R W, Vingarzan R, Mitchell H R, Goyette D, Sylvestre S. PAHs in the Fraser River basin: a critical appraisal PAH ratios as indicators of PAH source and composition. Organic Geochemistry, 2002, 33(4): 489–515

[30]

Pio C A, Alves C A, Duarte A C. Identification, abundance and origin of atmospheric organic particulate matter in a Portuguese rural area. Atmospheric Environment, 2001, 35(8): 1365–1375

[31]

Okuda T, Naoi D, Tenmoku M, Tanaka S, He K, Ma Y, Yang F, Lei Y, Jia Y, Zhang D. Polycyclic aromatic hydrocarbons (PAHs) in the aerosol in Beijing, China, measured by aminopropylsilane chemically-bonded stationary-phase column chromatography and HPLC/fluorescence detection. Chemosphere, 2006, 35(3): 427–435

[32]

Edoardo M. On-filter degradation of particle-bound benzo[a]pyrene by ozone during air sampling: a review of the experimental evidence of an artifact. Chemosphere, 2009, 77(10): 1275–1284

[33]

Pochl U. Formation and decomposition of hazardous chemical components contained in atmospheric aerosol particle. Journal of Aerosol Medicine, 2002, 15(2): 203–212

RIGHTS & PERMISSIONS

Higher Education Press and Springer-Verlag Berlin Heidelberg

AI Summary AI Mindmap
PDF (321KB)

2937

Accesses

0

Citation

Detail

Sections
Recommended

AI思维导图

/