A Case Study of Atmospheric Aerosols and Their Terrestrial Impacts Over China
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1 A Case Study of Atmospheric Aerosols and Their Terrestrial Impacts Over China W.L. Chameides Georgia Tech Aspen Global Change Institute August, 2000 Demographics & Land Use Industry & Agriculture Socio -Economic Drivers Atmospheric Responses CHINA-MAP Research at the Atmospheric-Biospheric- Metro-Agro Interface Using The Yangtze Delta, China As A Case Study Ecological Responses Climate Air Quality Agriculture Forests
2 Take Home s Is regional air quality affecting climate? Of course: regional haze Aerosol impact on climate is one outcome of regional air pollution. Could air quality interactions with climate affect projections of climate change? Aerosols affect solar radiation at earth s surface and thus can influence photosynthesis One outcome may be a change in C-storage by terrestrial ecosystems. Aerosols affect boundary layer dynamics Change in relative humidity can in turn affect aerosol radiative properties. Positive/negative feedback?
3 Aside: Aerosols, PM 2.5, and Light Scattering Estimated Light Scattering Coefficient (550 nm) vs. D p During Atlanta SuperSite Study Light Scattering Coefficient vs. PM2.5 during During Atlanta Supersite Study E scat = 3.8 +/ gm Δσ sp/δ logd p (µgm -3 µm -1 ) σ sp (Mm -1 ) D (µm) Aerosols having diameters > 2.5 µm do not contribute to light scattering TEOM PM2.5 Mass Conc. 3 )(ug/m PM2.5 mass is responsible for light scattering
4 The China-MAP Science Team USA USA Study Director: W. L. Chameides* 1 Co-Investigators: C. S. Kiang* 1 S. C. Liu* 1 Chao Luo* 1,9 Yan Huang* 1 J. St. John* 1 R. D. Saylor* 1 A. Steiner* 1 Hongbin Yu 1 G. Carmichael* 2 S. Guttikunda* 2 F. Giorgi* 3,4 Xunqiang Bi 3 Yun Qian 3 Jianhua Qian 4 L. Mearns* 4 D. Streets* 5 S. Waldhoff* 5 Mian Chin 6 D. Blake 7 M. Bergin 1 K. Baumann 1 H. Levy II 8 P. Kasibhatla 9 D. Cohan 1 * Funded by NASA EOS/IWG China China Study Director: Zhou Xiuji 10 Co-Investigators: Chen Longxun 10 Li xingsheng 10 Li Weiliang 10 Mao Jietai 11 Tang Xiaoyan 11 Tian Guoliang 12 Qin Yu 11 Wang Chunyi 10 Wang Rusong 12 Zhang Yuanhang 12 Japan Japan Study Director: H. Akimoto 13 Co-Investigators: H. Bandow 14 N. Katanani 15 H. Ueda 16 1 Georgia Institute of Technology 2 University of Iowa 3 Abdus Salam International Centre for Theoretical Physics 4 National Center for Atmospheric Research 5 Argonne National Laboratory 6 NASA 7 University of California at Irvine 8 Geophysical Fluid Dynamics Laboratory 9 Duke University 10 Chinese Academy of Meteorological Sciences 11 Peking University 12 Chinese Academy of Sciences 13 University of Tokyo 14 Osaka Prefectural University 15 Yamanashi University 16 Kyoto University
5 Haze in China: Early December, 1998
6 Haze in China: Early December, 1998
7 1999/ Month Yangtze Delta Field Experiment 32.5N 118E 32.5N 122E Jianhu Site (operated by FU/BU) [1/2 yr] Juyong Site (operated by CAMS) [1/2 yr] Nanxung Chang Shu Site (operated by CAMS) Tai Hu Lake Qingpu Site (operated by FU/BU) [To be visited by US Team] Shanghai Huang San Site (operated by Univ. Tokyo) Linan Site (operated by HKPU) [To be visited by US Team] Jiaxing Site (operated by FU/BY) [ozone only] 29.8N 118E 29.8N 122E
8 Linan Site Operated By HKPU Qingpu Site Operated By Fudan and Beijing Universities
9 Summary of Fine Particles Measurements; Yangtze, November, 1999 Average Observations [PM 2.5 ] = 102 ug/m 3 [AOD] = 0.6 [w] = 0.9 SO4 23.5% Others 0.8% NO3 8.5% NH4 9.5% Na 3.3% EC 5.3% OC 49.2%
10 What are the PM sources? What are the PM effects?
11 What are the PM sources? What are the PM effects? Emission RADM Tracer distribution (NOx, SOx, O3, etc) Prototype CHINA-MAP MODELING SYSTEM Meteorological fields Oxidant (OH, H2O2) ECMWF or CCM data as initial and boundary conditions Aerosol/Climate Coupled Model REG-CM With Aerosol Scheme Ozone pollution Meteorological & Radiation Fields C a n b e r u n i n c l i m a t e Crop o Yield Model r m e t e o r o l o g i c a l m o
12
13 Obs: ~ 0.6
14 Observed PM 2.5 Composition (Linan) (PM 2.5 ~ 100 ug/m 3 ) Model-calculated PM Composition (Linan) (PM ~ 75 ug/m 3 ) Sulfate 23.5% Others 0.8% Sulfate 34% OC 31% OC 49.2% Nitrate 8.5% Ammonium 9.5% Sodium 3.3% EC 5.3% Nitrate 18% EC 7% Ammonium 10%
15 Obs: ~100 ug/m 3
16 Obs: ~ 0.9
17 Need for an additional heterogeneous SO 2 -to-so 4 = conversion pathway Obs: ~ 1 ppbv/ppbv
18 Radiative forcing exceeds 60 W/m 2
19 Significant aerosol-induced temperature decreases predicted from direct effect in regions of China where records indicate downward temperature trends
20 Evidence of the Indirect Effect? ISCCP COD vs. Model AOD Model COD vs. Model AOD with and without indirect effect
21 Is perturbation to physical climate only environmental consequence of aerosol loadings? PAR/cos( µ ) (W/m2) PAR/cos(µ) = τ/cos(µ) R 2 = τ /cos( µ ) ( λ = 500 nm)
22 PM and PAR in China PAR/cos( µ) (W/m2) PAR/cos(µ) = τ/cos(µ) R 2 = 0.82 Simple Rule of Thumb PAR ~ 450cos(µ) 80τ For each 0.1 increment in τ, PAR reduced by ~ 8 W/m 2 In Eastern China τ ~ So ΔPAR ~ W/m τ /cos( µ ) ( λ = 500 nm) PAR ~ W/m 2 So ΔPAR/PAR ~ 5 30%
23 Regional Haze and Photosynthesis We estimate that aerosols are reducing surface solar irradiance by ~ 5-30% Does that have any effect on photosynthesis? Crop yields C storage in forests % Reduction in Surface Solar Radiance
24 Brief Primer on Photosynthesis -- 2-Step Process -- Carboxylation: Rubisco or nutrient limited step Phosphorylization: Light limited step
25 Regional Haze and Photosynthesis Effect of aerosols depends upon whether photosynthetic rates are in light-limited regime.
26 Regional Haze and Photosynthesis Effect of aerosols depends upon whether photosynthetic rates are in light-limited regime. If there are adequate nutrients (e.g., N), plant will simply increase carboxylase or rubisco activity as light intensity increases to optimize productivity. Under these conditions, increase in aerosols should decrease productivity
27 Regional Haze and Photosynthesis: The Simple Picture In fact, agricultural field data generally show that for each 1% reduction in irradiance, there is ~ 1% reduction in crop yields Crop response models for rice and wheat tuned to conditions appropriate for agricultural fields in China indicate a similar effect. Model-Calculated Yields (Nanjing) Rice Wheat Crop Yield Ch Total Surface Solar Irradiance (% of observed irradiance) Implication: Mitigation of aerosols and regional haze in China could produce a 5-30% increase in optimal crop yields in China.
28 Regional Haze and Photosynthesis: The More Complex Picture Effect of aerosols depends upon whether photosynthetic rates are in light-limited regime. In ecosystems with nutrient limitation (e.g., unmanaged ecosystems) plants can not routinely increase carboxylase or rubisco activity. Under these conditions, sunlit leaves are generally in the light saturated regime, while shaded leaves are not. Shaded leaves Sunlit leaves Thus, an increase in aerosols could cause an increase or decrease in productivity
29 Regional Haze and Photosynthesis It is possible that aerosols and regional haze cause an increase in photosynthesis (and C storage) under some conditions. Less radiation, but more efficient use of the radiation PAR/cos( µ) (W/m2) PAR/cos(µ) = τ/cos(µ) R 2 = τ /cos( µ ) ( λ = 500 nm)
30 Regional Haze and Photosynthesis Photosynthesis models with static leaf properties predict both increases and decreases depending upon conditions Norman Model (constant N) g CO2/m2/day AOD=0.05 AOD=0.25 AOD=0.5 0 Clear Sky Cloud (COD=2)
31 Regional Haze and Photosynthesis Experimental results often indicate increasing C uptake with increased diffuse radiation Subtropical field experiment for grasses using solarweave as a surrogate for clouds/aerosols
32 Regional Haze and Photosynthesis Experimental results often indicate increasing C uptake with increased diffuse radiation but, up to a point
33 Regional Haze and Photosynthesis Also important to bear in mind that increases in C uptake do not necessarily translate into increased grain yield --- it depends on C allocation Experiment on Sunflowers Using Solarweave Shaded/Sun Biomass Harvest Index Yield
34 Another Complication: Insoluble particles Io,p / I o,s EC (6 ug/m^3) IM (60 ug/m^3) EC+IM SEM image of particles deposited to an SEM grid mounted on leaf in Yangtze Delta region of China over 2-week period Time (Days) Estimation of light transmission at leaf surface with time due to dry deposition of elemental carbon (EC) and insoluble mass (IM) based on measurements in the Yangtze Delta region of China
35 Conclusions Anthropogenic emissions produce large fine particle loadings over much of eastern China PM ~ 100 ug/m 3 ~ 50% is organic C In summer and fall mineral aerosol is a small contribution to total scattering Significant gradients on spatial scales of ~ 100 km Impact on terrestrial biosphere may be signficant Agriculture Carbon storage
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