GAO Jinghua, ZHOU Chunliang, HU Jianxiong, MENG Ruilin, ZHOU Maigeng, HOU Zhulin, XIAO Yize, YU Min, HUANG Biao, XU Xiaojun, LIU Tao, GONG Weiwei, JIN Donghui, QIN Mingfang, YIN Peng, XU Yiqing, HE Guanhao, WU Xianbo, ZENG Weilin, MA Wenjun. Construction of AQHI based on joint effects of multi-pollutants in 5 provinces of China[J]. Journal of Environmental and Occupational Medicine, 2023, 40(3): 281-288. DOI: 10.11836/JEOM22425
Citation: GAO Jinghua, ZHOU Chunliang, HU Jianxiong, MENG Ruilin, ZHOU Maigeng, HOU Zhulin, XIAO Yize, YU Min, HUANG Biao, XU Xiaojun, LIU Tao, GONG Weiwei, JIN Donghui, QIN Mingfang, YIN Peng, XU Yiqing, HE Guanhao, WU Xianbo, ZENG Weilin, MA Wenjun. Construction of AQHI based on joint effects of multi-pollutants in 5 provinces of China[J]. Journal of Environmental and Occupational Medicine, 2023, 40(3): 281-288. DOI: 10.11836/JEOM22425

Construction of AQHI based on joint effects of multi-pollutants in 5 provinces of China

  • Background Air pollution is a major public health concern. Air Quality Health Index (AQHI) is a very important air quality risk communication tool. However, AQHI is usually constructed by single-pollutant model, which has obvious disadvantages.
    Objective To construct an AQHI based on the joint effects of multiple air pollutants (J-AQHI), and to provide a scientific tool for health risk warning and risk communication of air pollution.
    Methods Data on non-accidental deaths in Yunnan, Guangdong, Hunan, Zhejiang, and Jilin provinces from January 1, 2013 to December 31, 2018 were obtained from the corresponding provincial disease surveillance points systems (DSPS), including date of death, age, gender, and cause of death. Daily meteorological (temperature and relative humidity) and air pollution data (SO2, NO2, CO, PM2.5, PM10, and maximum 8 h O3 concentrations) at the same period were respectively derived from China Meteorological Data Sharing Service System and National Urban Air Quality Real-time Publishing Platform. Lasso regression was first applied to select air pollutants, then a time-stratified case-crossover design was applied. Each case was matched to 3 or 4 control days which were selected on the same days of the week in the same calendar month. Then a distributed lag nonlinear model (DLNM) was used to estimate the exposure-response relationship between selected air pollutants and mortality, which was used to construct the AQHI. Finally, AQHI was classified into four levels according to the air pollutant guidance limit values from World Health Organization Global Air Quality Guidelines (AQG 2021), and the excess risks (ERs) were calculated to compare the AQHI based on single-pollutant model and the J-AQHI based on multi-pollutant model.
    Results PM2.5, NO2, SO2, and O3 were selected by Lasso regression to establish DLNM model. The ERs for an interquartile range (IQR) increase and 95% confidence intervals (CI) for PM2.5, NO2, SO2 and O3 were 0.71% (0.34%–1.09%), 2.46% (1.78%–3.15%), 1.25% (0.9%–1.6%), and 0.27% (−0.11%–0.65%) respectively. The distribution of J-AQHI was right-skewed, and it was divided into four levels, with ranges of 0-1 for low risk, 2-3 for moderate risk, 4-5 for high health risk, and ≥6 for severe risk, and the corresponding proportions were 11.25%, 64.61%, 19.33%, and 4.81%, respectively. The ER (95%CI) of mortality risk increased by 3.61% (2.93–4.29) for each IQR increase of the multi-pollutant based J-AQHI , while it was 3.39% (2.68–4.11) for the single-pollutant based AQHI .
    Conclusion The J-AQHI generated by multi-pollutant model demonstrates the actual exposure health risk of air pollution in the population and provides new ideas for further improvement of AQHI calculation methods.
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