1. Space-based constraints on non-methane VOC emissions in Asia

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1 1. Space-based constraints on non-methane VOC emissions in Asia + 2. Sensitivity of summertime surface ozone to surface temperature over Southeastern U.S.: Interannual variability as a diagnostic for chemical transport models Tzung-May Fu (tmfu@pku.edu.cn) Dept. of Atmospheric & Oceanic Sciences, Peking University Yale + NUIST video conference April 19, 2013

2 Our research: Climate effects of reactive organics in the atmosphere Chemistry Climate Direct RF Indirect RF (clouds) Ozone, Secondary Organic Aerosols Climate and environmental changes Physical + chemical processes Non-methane VOC, Primary Organic Aerosols Emissions Surface 2

3 Role of atmospheric chemistry in the Earth system International Global Atmosphere Chemistry (2006) Science Plan and Implementation Strategy : 通过整合对大气过程及地球系统响应与反 馈的理解, 增进对未来数十年大气化学组分 的预测能力 IPCC 4 th Assessment (2007) : 要准确预测未来气候变化, 模式必须正确考虑气候与其他决定大气温室气体 高活性气体及气溶胶浓度过程的反馈作用 3

4 Non-methane Volatile Organic Compounds(NMVOCs) Precursor to tropospheric pollutants O 3 Secondary Organic Aerosol(SOA) Chemical processes Anthropogenic + Biomass burning VOCs ~150 Tg y -1? Biogenic VOCs 500~1200 Tg y -1? Isoprene 280 ~ 850 Tg y -1? Ocean VOCs ~20 Tg y -1? Land Ocean

5 I. Satellite observational constraints on VOC emissions VOCs oxidize HCHO ( 甲醛 ) Top-down constraints on VOC emissions [Fu et al., 2007] Satellites observe: trace gases(o 3, NO 2, HCHO, CHOCHO, CO, SO 2, ) aerosols GHG(CO 2,CH 4 ) meteorology & climate variables land surface

6 HCHO vertical columns observed from space constrain reactive VOC emissions GOME Retrieve HCHO vertical column HCHO Jul 1995 ~ Dec 2003 on board ERS-2 UV-backscatter Nadir viewing Global coverage in 3 days Resolution 320 km x 40 km HCHO, O 3, NO 2, BrO Reactive VOCs: lifetime < 1 day isoprene, alkenes, xylenes, HCHO (direct emission) Ω 1 iey k HCHO i HCHO i Ω HCHO VOCs OH, h k i, Y i HCHO OH, h k HCHO detection limit 300 km VOC source a-pinene alkanes Distance downwind Palmer et al. [2003,2006], JGR Fu et al. [2007], JGR

7 Current knowledge of VOC emissions in Asia NOT consistent with observations State-of-the-art bottom-up reactive VOC emission inventories GEOS-Chem Anthropogenic 40 Tg Streets et al. [2003] Biomass burning 12 Tg Streets et al. [2003] Biogenic 80 Tg Guenther et al. [2006] Global chemical transport model Assimilated meteorology Resolution: 2.5 longitude x 2 latitude GOME HCHO column June 1996~2001 Model HCHO column June 2001 [10 16 molec cm -2 ] Fu et al. [2007]

8 GOME HCHO Monthly Columns over Asia ( ) Fu et al. [2007] Relationship to VOC emissions far more complex than for N. America; biomass burning, isoprene, anthropogenic VOCs, direct HCHO emission all contribute

9 HCHO column [10 16 molec/cm2] Linear regression can separate biomass burning and biogenic emissions 3 Ω i i E E GOME 0 + nonlinear terms 1 i GOME Model background = 1 x biogenic + 2 biomass r 2 = 0.80 ~ 0.93 GOME GEOS-Chem Model bkgd Biogenic Biomass x 2 Anthropogenic x 2 Fu et al. [2007]

10 Excess winter GOME HCHO due to Chinese vehicle emissions GOME 25% higher than model 1:1 Inventory by Streets et al. [2003] Observation by Barletta et al. [2005] Sampled 43 Chinese cities in Jan and Feb 2001 Inventory underestimates pentane & xylenes Underestimates vehicular emissions Fu et al. [2007]

11 HCHO column [10 16 molec/cm2] HCHO seasonal variation dominated by biogenic and biomass burning emissions GOME GEOS-Chem Model bkgd Biogenic Biomass x 2 Anthropogenic x 2 Fu et al. [2007] Bottom-up inventories capture the timing but not the magnitude of emissions

12 Redistribution of biogenic isoprene GOME 56 Tg MEGAN 52 Tg GEIA 60 Tg [10 3 kg km -2 yr -1 ] Higher emission from the deciduous broadleaf forests in China Lower emission from the evergreen broadleaf forests in Indonesia Scaling factors GOME vs MEGAN Fu et al. [2007]

13 Fu et al. [2007] Biomass burning emission ~ 5 X current inventory! GOME 14 Tg Streets et al. 3.2 Tg Confirmed in Inomata [2007] [10 3 kg km -2 yr -1 ] Scaling factors GOME vs Streets Large emission from wheat residue burning in field!

14 Fu et al. [2007] E & S Asian reactive VOC emissions VOCs OH, NO 3, O 3 HCHO 11 (uncertainty 2x) 3.2 (uncertainty 3x) 52 (uncertainty 2x) 66 (uncertainty 3x) 12 ± 8 14 ± 4 56 ± ± 32 Top-down emission estimates Unit: [Tg y -1 ]

15 More NMVOCs + 5 ~ 20 ppb O 3 in China Mean afternoon O 3 at sfc w/ current inventories [O 3 ] using new inventory consistent with measurements [Gao et al., 2005] O 3 at surface w/ GOME w/ current inventories MAR SEP JUN DEC [ppb] chemistry NO x -saturated large O 3 NO x -limited, but large increase in NMVOC emission still drives HO x chemistry significant O 3 Strongly NO x -limited small O 3 Fu et al. [2007]

16 Thank you! Please come visit the Dept of Atmospheric and Oceanic Sciences at Peking University!

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