State Key Joint Laboratory of Environment Simulation and Pollution Control, School of Environment, Tsinghua University, Beijing 100084, China.
Department of Mathematical Sciences, Tsinghua University, Beijing 100084, China.
Environ Pollut. 2018 Dec;243(Pt B):1710-1718. doi: 10.1016/j.envpol.2018.09.089. Epub 2018 Sep 21.
The estimation of PM-related mortality is becoming increasingly important. The accuracy of results is largely dependent on the selection of methods for PM exposure assessment and Concentration-Response (C-R) function. In this study, PM observed data from the China National Environmental Monitoring Center, satellite-derived estimation, widely collected geographic and socioeconomic information variables were applied to develop a national satellite-based Land Use Regression model and evaluate PM exposure concentrations within 2013-2015 with the resolution of 1 km × 1 km. Population weighted concentration declined from 72.52 μg/m in 2013 to 57.18 μg/m in 2015. C-R function is another important section of health effect assessment, but most previous studies used the Integrated Exposure Regression (IER) function which may currently underestimate the excess relative risk of exceeding the exposure range in China. A new Shape Constrained Health Impact Function (SCHIF) method, which was developed from a national cohort of 189,793 Chinese men, was adopted to estimate the PM-related premature deaths in China. Results showed that 2.19 million (2013), 1.94 million (2014), 1.65 million (2015) premature deaths were attributed to PM long-term exposure, different from previous understanding around 1.1-1.7 million. The top three provinces of the highest premature deaths were Henan, Shandong, Sichuan, while the least ones were Tibet, Hainan, Qinghai. The proportions of premature deaths caused by specific diseases were 53.2% for stroke, 20.5% for ischemic heart disease, 16.8% for chronic obstructive pulmonary disease and 9.5% for lung cancer. IER function was also used to calculate PM-related premature deaths with the same exposed level used in SCHIF method, and the comparison of results indicated that IER had made a much lower estimation with less annual amounts around 0.15-0.5 million premature deaths within 2013-2015.
PM 相关死亡率的估算变得越来越重要。结果的准确性在很大程度上取决于 PM 暴露评估方法和浓度-反应(C-R)函数的选择。本研究应用中国国家环境监测中心的 PM 观测数据、卫星衍生估计值以及广泛收集的地理和社会经济信息变量,开发了一个全国性的基于卫星的土地利用回归模型,并评估了 2013-2015 年 1km×1km 分辨率下的 PM 暴露浓度。2013 年至 2015 年,人口加权浓度从 72.52μg/m 下降至 57.18μg/m。C-R 函数是健康效应评估的另一个重要部分,但大多数先前的研究使用综合暴露回归(IER)函数,该函数可能会低估中国暴露范围超标的超额相对风险。本研究采用了一种新的形状约束健康影响函数(SCHIF)方法,该方法是从一项覆盖 189793 名中国男性的全国性队列中发展而来,用于估计中国的 PM 相关过早死亡人数。结果表明,2013 年、2014 年和 2015 年分别有 219 万、194 万和 165 万人的过早死亡归因于 PM 长期暴露,与之前的认识(110 万至 170 万人)不同。过早死亡人数最多的三个省份是河南、山东和四川,而最少的三个省份是西藏、海南和青海。由特定疾病引起的过早死亡比例为中风 53.2%、缺血性心脏病 20.5%、慢性阻塞性肺疾病 16.8%和肺癌 9.5%。IER 函数也用于计算与 SCHIF 方法中使用的相同暴露水平相关的 PM 相关过早死亡人数,结果比较表明,IER 函数的估计值要低得多,在 2013-2015 年期间,每年的过早死亡人数约为 0.15-0.5 万。