Effects of reactive hydrocarbons on ozone formation in southern Taiwan

被引:72
作者
Chang, CC
Chen, TY
Lin, CY
Yuan, CS
Liu, SC
机构
[1] Acad Sinica, Res Ctr Environm Changes, Taipei 11529, Taiwan
[2] Natl Sun Yat Sen Univ, Inst Environm Engn, Kaohsiung 804, Taiwan
关键词
ozone formation potential; non-methane hydrocarbons; emission sources;
D O I
10.1016/j.atmosenv.2004.12.042
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Ambient air samples were collected at 13 air quality monitoring stations in Kaohsiung city, Kaohsiung county, and Pingtung county (KKP) to investigate the composition and spatial distribution of C-2-C-10 non-methane hydrocarbons (NMHCs) in southern Taiwan. Ozone formation potentials (OFPs) of NMHCs were estimated using maximum incremental reactivity (MIR) and k(OH) method (reactivity of NMHC with OH radical) to assess the relative effects of hydrocarbons on ozone formation. The measurements showed that mixing ratios of toluene, ethene, ethyne, ethane, isopantane and propane were the highest among all measured species at most of the sampling sites. Nevertheless, considering both the photochemical reactivities and mixing ratios of all the measured species, toluene, xylene, ethene and propene were calculated to have the highest OFPs and reactivities. The OFPs and reactivities assessed by the MIR and k(OH) methods for the four compounds accounted for 54.5% and 39.3% of all the measured species. Larger benefit margin of ozone abatement may be obtained by reducing emissions of a group of key species with high OFPs. 2,2-dimethylbutane (22DMC4) was used as an indicator of traffic emissions to distinguish traffic from non-traffic contributions of key species in Kaohsiung metropolitan area. It revealed that the contribution of non-traffic source was significant for toluene, whereas xylene was found to be primarily from the traffic source in Kaohsiung metropolitan area during the sampling periods. (c) 2005 Elsevier Ltd. All rights reserved.
引用
收藏
页码:2867 / 2878
页数:12
相关论文
共 27 条
[1]   WINTERTIME SOURCE-RECONCILIATION OF AMBIENT ORGANICS [J].
ARONIAN, PF ;
SCHEFF, PA ;
WADDEN, RA .
ATMOSPHERIC ENVIRONMENT, 1989, 23 (05) :911-920
[2]   GAS-PHASE TROPOSPHERIC CHEMISTRY OF ORGANIC-COMPOUNDS - A REVIEW [J].
ATKINSON, R .
ATMOSPHERIC ENVIRONMENT PART A-GENERAL TOPICS, 1990, 24 (01) :1-41
[3]   An investigation into the traffic-related fraction of isoprene at an urban location [J].
Borbon, A ;
Fontaine, H ;
Veillerot, M ;
Locoge, N ;
Galloo, JC ;
Guillermo, R .
ATMOSPHERIC ENVIRONMENT, 2001, 35 (22) :3749-3760
[4]   COMPUTER MODELING STUDY OF INCREMENTAL HYDROCARBON REACTIVITY [J].
CARTER, WPL ;
ATKINSON, R .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1989, 23 (07) :864-880
[5]  
CARTER WPL, 1994, J AIR WASTE MANAGE, V44, P881
[6]   Assessment of traffic contribution to hydrocarbons using 2,2-dimethylbutane as a vehicular indicator [J].
Chang, CC ;
Chen, TY ;
Chou, C ;
Liu, SC .
TERRESTRIAL ATMOSPHERIC AND OCEANIC SCIENCES, 2004, 15 (04) :697-711
[7]   Analysis of methyl tert-butyl ether in the atmosphere and implications as an exclusive indicator of automobile exhaust [J].
Chang, CC ;
Lo, SJ ;
Lo, JG ;
Wang, JL .
ATMOSPHERIC ENVIRONMENT, 2003, 37 (34) :4747-4755
[8]  
CHANG KH, 1998, EPA87FA4203F5
[9]   Scientific basis for the VOC reactivity issues raised by Section 183(e) of the Clean Air Act Amendments of 1990 [J].
Dimitriades, B .
JOURNAL OF THE AIR & WASTE MANAGEMENT ASSOCIATION, 1996, 46 (10) :963-970
[10]   Measurement and analysis of C2-C10 hydrocarbons at Whiteface Mountain, New York [J].
Gong, Q ;
Demerjian, KL .
JOURNAL OF GEOPHYSICAL RESEARCH-ATMOSPHERES, 1997, 102 (D23) :28059-28069