Sources of organic aerosol investigated using organic compounds as tracers measured during CalNex in Bakersfield

被引:18
作者
Zhao, Yunliang [1 ]
Kreisberg, Nathan M. [2 ]
Worton, David R. [1 ,2 ]
Isaacman, Gabriel [1 ]
Gentner, Drew R. [3 ]
Chan, Arthur W. H. [1 ]
Weber, Robin J. [1 ]
Liu, Shang [4 ]
Day, Douglas A. [4 ]
Russell, Lynn M. [4 ]
Hering, Susanne V. [2 ]
Goldstein, Allen H. [1 ,3 ]
机构
[1] Univ Calif Berkeley, Dept Environm Sci Policy & Management, Berkeley, CA 94720 USA
[2] Aerosol Dynam Inc, Berkeley, CA USA
[3] Univ Calif Berkeley, Dept Civil & Environm Engn, Berkeley, CA 94720 USA
[4] Univ Calif San Diego, Scripps Inst Oceanog, San Diego, CA 92103 USA
基金
美国海洋和大气管理局;
关键词
POSITIVE MATRIX FACTORIZATION; AIR-POLLUTION SOURCES; GAS-PHASE REACTION; SOURCE APPORTIONMENT; ATMOSPHERIC AEROSOL; PARTICULATE MATTER; SECONDARY; EMISSIONS; PM2.5; MASS;
D O I
10.1002/jgrd.50825
中图分类号
P4 [大气科学(气象学)];
学科分类号
0706 ; 070601 ;
摘要
To investigate the major sources of summertime organic aerosol (OA) and provide insights into secondary organic aerosol (SOA) formation, positive matrix factorization analysis was performed on a large set of organic species measured during the California at the Nexus of Air Quality and Climate Change (CalNex) campaign in Bakersfield, CA. Six OA source factors were identified, including one representing primary organic aerosol (POA); four different types of SOA representing local, regional, and nighttime production; and one representing a complex mixture of additional OA sources that were not further resolvable. POA accounted for an average of 15% of measured OA. The complex mixture of additional OA sources contributed an average of 13% of measured OA. The combined contribution of four types of SOA to measured OA averaged 72% and varied diurnally from 78% during the day to 66% at night. Both regional and local SOA were significant contributors to measured OA during the day, but regional SOA was the larger one, especially in the afternoon. Although contributions to SOA from oxidation of biogenic gas-phase compounds were less constrained, they were evident and dominantly occurred at night. The formation of SOA is indicated to be mainly through gas-to-particle condensation of gas-phase oxidation products during the day. Our results indicate that effective control measures to reduce summertime OA in Bakersfield should focus on reducing sources of gas-phase organics that serve as SOA precursors during the day, and it is more effective to reduce SOA precursors at the regional scale in the afternoon. Key Points SOA was the dominant component of OA, and four types of SOA were identified Both regional and local SOA were significant contributors to OA the formation of SOA was mainly through gas-to-particle condensation ©2013. American Geophysical Union. All Rights Reserved.
引用
收藏
页码:11388 / 11398
页数:11
相关论文
共 48 条
[1]   Atmospheric degradation of volatile organic compounds [J].
Atkinson, R ;
Arey, J .
CHEMICAL REVIEWS, 2003, 103 (12) :4605-4638
[2]   To What Extent Can Biogenic SOA be Controlled? [J].
Carlton, Annmarie G. ;
Pinder, Robert W. ;
Bhave, Prakash V. ;
Pouliot, George A. .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2010, 44 (09) :3376-3380
[3]   Diurnal variations of individual organic compound constituents of ultrafine and accumulation mode particulate matter in the Los Angeles basin [J].
Fine, PM ;
Chakrabarti, B ;
Krudysz, M ;
Schauer, JJ ;
Sioutas, C .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2004, 38 (05) :1296-1304
[4]   Elucidating secondary organic aerosol from diesel and gasoline vehicles through detailed characterization of organic carbon emissions [J].
Gentner, Drew R. ;
Isaacman, Gabriel ;
Worton, David R. ;
Chan, Arthur W. H. ;
Dallmann, Timothy R. ;
Davis, Laura ;
Liu, Shang ;
Day, Douglas A. ;
Russell, Lynn M. ;
Wilson, Kevin R. ;
Weber, Robin ;
Guha, Abhinav ;
Harley, Robert A. ;
Goldstein, Allen H. .
PROCEEDINGS OF THE NATIONAL ACADEMY OF SCIENCES OF THE UNITED STATES OF AMERICA, 2012, 109 (45) :18318-18323
[5]   Biogenic carbon and anthropogenic pollutants combine to form a cooling haze over the southeastern United States [J].
Goldstein, Allen H. ;
Koven, Charles D. ;
Heald, Colette L. ;
Fung, Inez Y. .
PROCEEDINGS OF THE NATIONAL ACADEMY OF SCIENCES OF THE UNITED STATES OF AMERICA, 2009, 106 (22) :8835-8840
[6]   PRODUCTS OF THE OH RADICAL-INITIATED GAS-PHASE REACTION OF FLUORENE IN THE PRESENCE OF NOX [J].
HELMIG, D ;
AREY, J ;
ATKINSON, R ;
HARGER, WP ;
MCELROY, PA .
ATMOSPHERIC ENVIRONMENT PART A-GENERAL TOPICS, 1992, 26 (09) :1735-1745
[7]   OH RADICAL-INITIATED GAS-PHASE REACTION-PRODUCTS OF PHENANTHRENE [J].
HELMIG, D ;
HARGER, WP .
SCIENCE OF THE TOTAL ENVIRONMENT, 1994, 148 (01) :11-21
[8]   Recent developments in receptor modeling [J].
Hopke, PK .
JOURNAL OF CHEMOMETRICS, 2003, 17 (05) :255-265
[9]   Positive matrix factorization (PMF) analysis of molecular marker measurements to quantify the sources of organic aerosols [J].
Jaeckels, Jeffrey M. ;
Bae, Min-Suk ;
Schauer, James J. .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2007, 41 (16) :5763-5769
[10]   Heterogeneous atmospheric aerosol production by acid-catalyzed particle-phase reactions [J].
Jang, MS ;
Czoschke, NM ;
Lee, S ;
Kamens, RM .
SCIENCE, 2002, 298 (5594) :814-817