Biogenic emission measurement and inventories determination of biogenic emissions in the eastern United States and Texas and comparison with biogenic emission inventories

被引:77
作者
Warneke, C. [1 ,2 ]
de Gouw, J. A. [1 ,2 ]
Del Negro, L. [3 ]
Brioude, J. [1 ,2 ]
McKeen, S. [1 ,2 ]
Stark, H. [1 ,2 ]
Kuster, W. C. [1 ]
Goldan, P. D. [1 ]
Trainer, M. [1 ]
Fehsenfeld, F. C. [1 ,2 ]
Wiedinmyer, C. [4 ]
Guenther, A. B. [4 ]
Hansel, A. [5 ]
Wisthaler, A. [5 ]
Atlas, E. [6 ]
Holloway, J. S. [1 ,2 ]
Ryerson, T. B. [1 ]
Peischl, J. [1 ,2 ]
Huey, L. G. [7 ]
Hanks, A. T. Case [8 ]
机构
[1] NOAA, Div Chem Sci, ESRL, Boulder, CO USA
[2] Univ Colorado, CIRES, Boulder, CO 80309 USA
[3] Lake Forest Coll, Dept Chem, Lake Forest, IL 60045 USA
[4] NCAR, ACD, Boulder, CO USA
[5] Univ Innsbruck, Inst Ionenphys & Angew Phys, A-6020 Innsbruck, Austria
[6] Univ Miami, Rosenstiel Sch Marine & Atmospher Sci, Marine & Atmospher Chem Div, Miami, FL 33149 USA
[7] Georgia Inst Technol, Sch Earth & Atmospher Sci, Atlanta, GA 30332 USA
[8] Univ Louisiana Monroe, Dept Geosci, Monroe, LA USA
关键词
ISOPRENE EMISSIONS; ORGANIC-COMPOUNDS; OZONE FORMATION; MODEL; HYDROCARBONS; VALIDATION; CHEMISTRY; CAPACITY; MEGAN;
D O I
10.1029/2009JD012445
中图分类号
P4 [大气科学(气象学)];
学科分类号
0706 ; 070601 ;
摘要
During the NOAA Southern Oxidant Study 1999 (SOS1999), Texas Air Quality Study 2000 (TexAQS2000), International Consortium for Atmospheric Research on Transport and Transformation (ICARTT2004), and Texas Air Quality Study 2006 (TexAQS2006) campaigns, airborne measurements of isoprene and monoterpenes were made in the eastern United States and in Texas, and the results are used to evaluate the biogenic emission inventories BEIS3.12, BEIS3.13, MEGAN2, and WM2001. Two methods are used for the evaluation. First, the emissions are directly estimated from the ambient isoprene and monoterpene measurements assuming a well-mixed boundary layer and are compared with the emissions from the inventories extracted along the flight tracks. Second, BEIS3.12 is incorporated into the detailed transport model FLEXPART, which allows the isoprene and monoterpene mixing ratios to be calculated and compared to the measurements. The overall agreement for all inventories is within a factor of 2 and the two methods give consistent results. MEGAN2 is in most cases higher, and BEIS3.12 and BEIS3.13 lower than the emissions determined from the measurements. Regions with clear discrepancies are identified. For example, an isoprene hot spot to the northwest of Houston, Texas, was expected from BEIS3 but not observed in the measurements. Interannual differences in emissions of about a factor of 2 were observed in Texas between 2000 and 2006.
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页数:21
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