Journal
ATMOSPHERIC ENVIRONMENT
Volume 152, Issue -, Pages 389-404Publisher
PERGAMON-ELSEVIER SCIENCE LTD
DOI: 10.1016/j.atmosenv.2016.12.053
Keywords
Urbanization; Land-use; South China; Meteorological conditions; Air quality; WRF/Chem
Funding
- National Natural Science Foundation of China [41475122, 91544230, 41621005]
- Key Laboratory of South China Sea Meteorological Disaster Prevention and Mitigation of Hainan Province [SCSF201401]
- National Key Research and Development Program of China [2016YFC0203303]
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The change of land-use from natural to artificial surface induced by urban expansion can deeply impact the city environment. In this paper, the model WRF/Chem is applied to explore the effect of this change on regional meteorology and air quality over South China, where people have witnessed a rapid rate of urbanization. Two sets of urban maps are adopted to stand for the pre-urbanization and the present urban land-use distributions. Month-long simulations are conducted for January and July, 2014. The results show that urban expansion can obviously change the weather conditions around the big cities of South China. Especially in the Pearl River Delta region (PRD), the urban land-use change can increase the sensible heat flux by 40 W/m(2) in January and 80 W/m(2) in July, while decrease the latent heat flux about 50 W/m(2) in January and -120 W/m(2) in July. In the consequent, 2-m air temperature (T2) increases as much as 1 degrees C and 2 degrees C (respective to January and July), planetary boundary layer height (PBLH) rises up by 100-150 m and 300 m, 10-m wind speed (WS10) decreases by -1.2 m/s and -0.3 m/s, and 2m specific humidity is reduced by -0.8 g/kg and -1.5 g/kg. Also, the precipitation in July can be increased as much as 120 mm, with more heavy rains and rainstorms. These variations of meteorological factors can significantly impact the spatial and vertical distribution of air pollutants as well. In PRD, the enhanced updraft can reduce the surface concentrations of PM10 by 40 mu g/m(3) (30%) in January and -80 mu g/m(3) (50%) in July, but produce a correlating increase in the concentrations at higher atmospheric layers. However, according to the increase in T-2 and the decrease in surface NO, the surface concentrations of O-3 in PRD can increase by 2-6 ppb in January and 8-12 ppb in July. Meanwhile, there is a significant increase in the O-3 concentrations at upper layers above PRD, which should be attributed to the increase in air temperature and the enhanced upward transport of O-3 and its precursors. As for some relative small cities, such as Haikou, there is very little variation in surface PM10 and O-3 in both months, implying less urbanization in these areas. Moreover, the depletion of O-3 by NO may be the main cause of the reduction of O-3 at upper layers in these small cities. (C) 2016 Elsevier Ltd. All rights reserved.
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