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CMAQ APPLICATION TO OZONE POLLUTION IN THE
PEARL RIVER DELTA OF CHINA
Wei Zhou1,2 ,Yuanghang Zhang1,Xuesong Wang1,Daniel Cohan2 1.College of Environmental Science and Engineering, Peking
University, Beijing,China 2.Department of Civil and Environmental Engineering, Rice
University, Houston, TXPresented at the
Sixth Annual CMAS Conference, October 1-3, 2007, Chapel Hill, NC
Overview
• Ozone pollution in the Pearl River Delta (PRD)
• Emission and land-sea breeze in PRD
• CMAQ modeling for October 2004
• Ozone distribution and transport in Pearl River Estuary (PRE)
• Process Analysis (PA) of Ozone formation in PRE
Ozone Pollution in PRD
• NAAQS-O3: 200ug/m3 (93ppb)-1hr
• PRIDE_PRD: October, 2004
• Max O3 concentration :178ppb at Donghu
• Hot spot - Southwest of PRD and PRE
• At most sites, max O3 concentrations were higher than NAAQS
A: Guangzhou
C: Donghu
B: Xinken
The monitoring sites in the Program Regional Integrated Experiments of
Air Quality over Pearl River Delta (PRIDE_PRD), October 2004
Guangzhou
XinkenDonghu
Background wind
Configuration of Model-3/CMAQ • CMAQ: three nesting domains, 36km-12km-4km, v4.5, SAPRC-99, 13
vertical Layers, modeling period:17 – 23 October, 2004
• MM5: three modeling domains, 34 sigma levels
• Emission data : domain1: TRACE-P emission inventory 2000, domain2 & domain3:Hong Kong EPD 2001
Emission of NOx and VOC in PRD
NOx Emission at 14:00, October 17 VOC Emission at 14:00, October 17
The urban areas of Guangzhou, Shenzhen and Hong Kong are the main origins of NOx and VOC emission
CMAQ modeling -ozone simulation vs measurement
Guangzhou (Urban site)
Xinken(Rural site)
Donghu (Downwind site)
Regional ozone distribution in PRD
• Downwind of Guangzhou : ozone pollution hot spot
• Pearl River Estuary: high ozone concentration
• Metropolitan area: relatively low ozone concentration
A
B
At 14:00, October 17 2004Plot the vertical ozone profiles along lines A and B
Guangzhou
Vertical ozone profiles over PRE
Ozone profile along Line A( longitudinal transect )
Ozone profile along Line B(latitudinal transect)
The black square is Xinken
What drives the vertical distribution and high concentration of ozone over PRE ?
• No direct large emission sources of VOC and NOx
• What about the meteorological field over PRE – strong air circulations and land-sea breeze
• Can the land-sea breeze influence the ozone transport over PRE?
Land-sea breeze development in PRD
8:00, October 17 10:00, October 1714:00, 17 October20:00, 17 October
Vertical structure of land-sea breeze – latitudinal transect
• Air circulation existed over PRE : latitudinal transect
• At both banks of PRE, the horizontal wind speed is low, the vertical wind is relatively strong
• The height of the air circulation is approximately 600m
(Red square is Xinken)
Sigma level
• Air circulation existed over PRE, along the longitude
• The height of the air circulation is approximately 600m
• Air circulation will greatly affect air pollutant transport and accumulation
(Red square is Xinken)
Vertical structure of land-sea breeze – longitudinal transectSigma level
Process analysis of ozone formation at Xinken
• Vertical diffusion and vertical advection –the principle contributors of ozone
• Horizontal advection – the principle consumer of ozone
Conclusion• Heavy NOx and VOC are emitted in Guangzhou, Shenzhen
and Hong Kong• A severe regional ozone episode in October 2004 is well
reproduced by MM5 and CMAQ• Regional high ozone concentration was located in downwind
of Guangzhou and PRE; the urban areas of Guangzhou had a relatively lower ozone concentration
• Analysis of the air circulation and ozone profiles indicates that the land-sea breeze had the greatest influence on ozone concentrations in PRE
Acknowledgement : We thank Dr. Yongtao Hu for setting up Acknowledgement : We thank Dr. Yongtao Hu for setting up the coarse domain modeling of this study.the coarse domain modeling of this study.