Characterization of the sources and processes of organic and inorganic aerosols in New York city with a high-resolution time-of-flight aerosol mass apectrometer

被引:319
作者
Sun, Y. -L. [1 ]
Zhang, Q. [1 ]
Schwab, J. J. [2 ]
Demerjian, K. L. [2 ]
Chen, W. -N. [3 ]
Bae, M. -S. [2 ]
Hung, H. -M. [4 ]
Hogrefe, O. [2 ]
Frank, B. [5 ]
Rattigan, O. V. [5 ]
Lin, Y. -C. [3 ]
机构
[1] Univ Calif Davis, Dept Environm Toxicol, Davis, CA 95616 USA
[2] SUNY Albany, Atmospher Sci Res Ctr, Albany, NY 12222 USA
[3] Acad Sinica, Res Ctr Environm Changes, Taipei 115, Taiwan
[4] Natl Taiwan Univ, Dept Atmospher Sci, Taipei 10764, Taiwan
[5] New York State Dept Environm Conservat, Div Air Resources, Albany, NY USA
关键词
POSITIVE MATRIX FACTORIZATION; SEMICONTINUOUS PM2.5 SULFATE; CHEMICAL-COMPOSITION; SOURCE APPORTIONMENT; MEXICO-CITY; ELEMENTAL COMPOSITION; HYDROCARBON-LIKE; MEAT COOKING; SPECTROMETER; PARTICULATE;
D O I
10.5194/acp-11-1581-2011
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Submicron aerosol particles (PM1) were measured in-situ using a High-Resolution Time-of-Flight Aerosol Mass Spectrometer during the summer 2009 Field Intensive Study at Queens College in New York, NY. Organic aerosol (OA) and sulfate are the two dominant species, accounting for 54% and 24%, respectively, of the total PM1 mass. The average mass-based size distribution of OA presents a small mode peaking at similar to 150 nm (D-va) and an accumulation mode (similar to 550 nm) that is internally mixed with sulfate, nitrate, and ammonium. The diurnal cycles of both sulfate and OA peak between 01:00-02:00 p. m. EST due to photochemical production. The average (+/-sigma) oxygen-to-carbon (O/C), hydrogen-to-carbon (H/C), and nitrogen-to-carbon (N/C) ratios of OA in NYC are 0.36 (+/- 0.09), 1.49 (+/- 0.08), and 0.012 (+/- 0.005), respectively, corresponding to an average organic mass-to-carbon (OM/OC) ratio of 1.62 (+/- 0.11). Positive matrix factorization (PMF) of the high resolution mass spectra identified two primary OA (POA) sources, traffic and cooking, and three secondary OA (SOA) components including a highly oxidized, regional low-volatility oxygenated OA (LV-OOA; O/C = 0.63), a less oxidized, semi-volatile SV-OOA (O/C = 0.38) and a unique nitrogen-enriched OA (NOA; N/C = 0.053) characterized with prominent CxH2x+2N+ peaks likely from amino compounds. Our results indicate that cooking and traffic are two distinct and mass-equivalent POA sources in NYC, together contributing similar to 30% of the total OA mass during this study. The OA composition is dominated by secondary species, especially during high PM events. SV-OOA and LV-OOA on average account for 34% and 30%, respectively, of the total OA mass. The chemical evolution of SOA in NYC appears to progress with a continuous oxidation from SV-OOA to LV-OOA, which is further supported by a gradual increase of O/C ratio and a simultaneous decrease of H/C ratio in total OOA. Detailed analysis of NOA (5.8% of OA) presents evidence that organic nitrogen species such as amines might have played an important role in the atmospheric processing of OA in NYC, likely involving both acid-base chemistry and photochemistry. In addition, analysis of air mass trajectories and satellite imagery of aerosol optical depth (AOD) indicates that the high potential source regions of secondary sulfate and aged OA are mainly located in regions to the west and southwest of the city.
引用
收藏
页码:1581 / 1602
页数:22
相关论文
共 93 条
[31]   Atmospheric amines - Part I. A review [J].
Ge, Xinlei ;
Wexler, Anthony S. ;
Clegg, Simon L. .
ATMOSPHERIC ENVIRONMENT, 2011, 45 (03) :524-546
[32]   Atmospheric amines - Part II. Thermodynamic properties and gas/particle partitioning [J].
Ge, Xinlei ;
Wexler, Anthony S. ;
Clegg, Simon L. .
ATMOSPHERIC ENVIRONMENT, 2011, 45 (03) :561-577
[33]   Aged organic aerosol in the Eastern Mediterranean: the Finokalia Aerosol Measurement Experiment-2008 [J].
Hildebrandt, L. ;
Engelhart, G. J. ;
Mohr, C. ;
Kostenidou, E. ;
Lanz, V. A. ;
Bougiatioti, A. ;
DeCarlo, P. F. ;
Prevot, A. S. H. ;
Baltensperger, U. ;
Mihalopoulos, N. ;
Donahue, N. M. ;
Pandis, S. N. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2010, 10 (09) :4167-4186
[34]   Semicontinuous PM2.5 sulfate and nitrate measurements at an urban and a rural location in New York:: PMTACS-NY summer 2001 and 2002 campaigns [J].
Hogrefe, O ;
Schwab, JJ ;
Drewnick, F ;
Lala, GG ;
Peters, S ;
Demerjian, KL ;
Rhoads, K ;
Felton, HD ;
Rattigan, OV ;
Husain, L ;
Dutkiewicz, VA .
JOURNAL OF THE AIR & WASTE MANAGEMENT ASSOCIATION, 2004, 54 (09) :1040-1060
[35]   Highly time-resolved chemical characterization of atmospheric submicron particles during 2008 Beijing Olympic Games using an Aerodyne High-Resolution Aerosol Mass Spectrometer [J].
Huang, X. -F. ;
He, L. -Y. ;
Hu, M. ;
Canagaratna, M. R. ;
Sun, Y. ;
Zhang, Q. ;
Zhu, T. ;
Xue, L. ;
Zeng, L. -W. ;
Liu, X. -G. ;
Zhang, Y. -H. ;
Jayne, J. T. ;
Ng, N. L. ;
Worsnop, D. R. .
ATMOSPHERIC CHEMISTRY AND PHYSICS, 2010, 10 (18) :8933-8945
[36]   Design, modeling, optimization, and experimental tests of a particle beam width probe for the aerodyne aerosol mass spectrometer [J].
Huffman, JA ;
Jayne, JT ;
Drewnick, F ;
Aiken, AC ;
Onasch, T ;
Worsnop, DR ;
Jimenez, JL .
AEROSOL SCIENCE AND TECHNOLOGY, 2005, 39 (12) :1143-1163
[37]  
IOWIK JG, 2004, AEROSOL SCI TECH, V38, P1206
[38]   Development of an aerosol mass spectrometer for size and composition analysis of submicron particles [J].
Jayne, JT ;
Leard, DC ;
Zhang, XF ;
Davidovits, P ;
Smith, KA ;
Kolb, CE ;
Worsnop, DR .
AEROSOL SCIENCE AND TECHNOLOGY, 2000, 33 (1-2) :49-70
[39]   Evolution of Organic Aerosols in the Atmosphere [J].
Jimenez, J. L. ;
Canagaratna, M. R. ;
Donahue, N. M. ;
Prevot, A. S. H. ;
Zhang, Q. ;
Kroll, J. H. ;
DeCarlo, P. F. ;
Allan, J. D. ;
Coe, H. ;
Ng, N. L. ;
Aiken, A. C. ;
Docherty, K. S. ;
Ulbrich, I. M. ;
Grieshop, A. P. ;
Robinson, A. L. ;
Duplissy, J. ;
Smith, J. D. ;
Wilson, K. R. ;
Lanz, V. A. ;
Hueglin, C. ;
Sun, Y. L. ;
Tian, J. ;
Laaksonen, A. ;
Raatikainen, T. ;
Rautiainen, J. ;
Vaattovaara, P. ;
Ehn, M. ;
Kulmala, M. ;
Tomlinson, J. M. ;
Collins, D. R. ;
Cubison, M. J. ;
Dunlea, E. J. ;
Huffman, J. A. ;
Onasch, T. B. ;
Alfarra, M. R. ;
Williams, P. I. ;
Bower, K. ;
Kondo, Y. ;
Schneider, J. ;
Drewnick, F. ;
Borrmann, S. ;
Weimer, S. ;
Demerjian, K. ;
Salcedo, D. ;
Cottrell, L. ;
Griffin, R. ;
Takami, A. ;
Miyoshi, T. ;
Hatakeyama, S. ;
Shimono, A. .
SCIENCE, 2009, 326 (5959) :1525-1529
[40]  
*JPL, 2009, CHEM KIN PHOT DAT US, V16