Abstract

The Sichuan Basin (SCB) is located in southwestern China and has a total population of 108.1 million across 18 cities, including the 2 largest in western China (Chengdu and Chongqing). As most air quality monitoring stations are located in urban areas, we simulated the PM2.5 (i.e., particulate matter with an aerodynamic diameter < 2.5 µm) and ozone (O3) in the entire SCB during winter (December 2014–February 2015) and summer (June–August 2015) by using the Weather Research and Forecasting (WRF) and the Community Multi-scale Air Quality (CMAQ) models. The simulated concentrations of 24-h PM2.5 and its major components generally agree with observations during both seasons, but the simulated 1-h and 8-h O3 are acceptable only for summer. Increasing in severity from the rim of the SCB to its inner areas, the PM2.5, as well as its major components, exhibits hotspots near the central urban areas of Chongqing and Chengdu, with concentrations of 150–200 µg m–3 and 40–60 µg m–3 during winter and summer, respectively. The 1-h and 8-h O3 exhibit no hotspots in the urban centers of Chongqing and Chengdu but show elevated levels in some rural and suburban areas (55–70 ppb and 65–80 ppb, respectively), including those on the western and southwestern rim of the SCB, and downwind of the urban center of Chongqing. Despite the great spatial variations in the PM2.5 and O3 concentrations, the vast majority of the basin fails to meet the WHO guidelines for 24-h PM2.5 (25 µg m–3) and 8-h O3 (~47 ppb) on > 70% of the days during winter and > 40% of the days during summer, respectively. Based on the aforementioned spatial patterns of the PM2.5 and O3 concentrations, and the wind directions within the basin, strictly controlling emissions originating in the SCB may greatly reduce PM2.5 and O3 concentrations within the basin.

Highlights

  • Air pollution is one of the most severe environmental problems in China

  • Despite the great spatial variations in the PM2.5 and O3 concentrations, the vast majority of the basin fails to meet the WHO guidelines for 24-h PM2.5 (25 μg m–3) and 8-h O3 (~47 ppb) on > 70% of the days during winter and > 40% of the days during summer, respectively

  • When using the benchmarks to assess model performance, it should be noted that the benchmarks are considered as quantitative measures to compare with previous studies and model performance is affected by model parameterizations, landforms, meteorological reanalysis data, etc

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Summary

Introduction

Aerosol and Air Quality Research, 19: 2308–2319, 2019 pollution, the Ministry of Environmental Protection of the People’s Republic of China (MEP) has grouped the areas that are most affected by air pollution in the country into 3 regions and 10 city clusters (MEP, 2013; Fig. S1), including (1) Beijing-Tianjin-Hebei (BTH), (2) Yangtze River Delta (YRD), (3) Pearl River Delta (PRD), (4) central regions of Liaoning Province, (5) Shandong Province, (6) Wuhan and its peripheral localities, (7) Changsha, Zhuzhou, and Xiangtan in Hunan Province, (8) the Chengdu-Chongqing city cluster in the Sichuan Basin (SCB), (9) western coast of the Taiwan Strait, (10) central and northern regions of Shansi Province, (11) Guanzhong Plain in Shanxi Province, (12) parts of Gansu and Ningxia Province, and (13) Urumqi in Xinjiang Province These areas cover 1.32 million km and have a population of 675 million, accounting for 14% of China’s land, 48% of the country’s population, 71% of national gross domestic product (GDP), 52% of national coal consumption, and 50% of the national emission of sulfur dioxide (SO2), NOx, particulate matter (PM), and volatile organic compounds (VOCs) (MEP, 2013). In 2015, annual PM2.5 concentrations measured in the 18 cities were in the range of 21–74 μg m–3 (Table S1), about 2–7 times of the World

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