Li Jinyue, Liang Fengchao, Liu Fangchao, Li Jianxin, Huang Keyong, Yang Xueli, Chen Shufeng, Cao Jie, Shen Chong, Zhao Liancheng, Li Ying, Hu Dongsheng, Wang Wending, Wu Jianbin, Huang Jianfeng, Lu Xiangfeng, Gu Dongfeng
Department of Epidemiology, Fuwai Hospital, National Center for Cardiovascular Diseases, Chinese Academy of Medical Sciences and Peking Union Medical College, Beijing 100037, China; National Clinical Research Center for Cardiovascular Diseases, State Key Laboratory of Cardiovascular Epidemiology, Chinese Academy of Medical Sciences, Beijing 100037, China.
School of Public Health and Emergency Management, Southern University of Science and Technology, Shenzhen 518055, China.
Environ Int. 2022 Dec;170:107624. doi: 10.1016/j.envint.2022.107624. Epub 2022 Nov 10.
Although both environmental and genetic factors were linked to coronary artery disease (CAD), the extent to which the association of air pollution exposure with CAD can be influenced by genetic risk was not well understood.
A total of 41,149 participants recruited from the project of Prediction for Atherosclerotic Cardiovascular Disease Risk in China (China-PAR) were included. Genetic risk scores of CAD were constructed based on 540 genetic variants. Long-term PM exposures were assessed by adopting satellite-based PM estimations at 1-km resolution. We used stratified Cox proportional hazards regression model to examine the impact of PM exposure and genetic risk on CAD risk, and further analyzed modification effect of genetic predisposition on association between PM exposure and CAD risk.
During a median of 13.01 years of follow-up, 1,373 incident CAD events were observed. Long-term PM exposure significantly increased CAD risk, and the hazard ratios (HRs) [95% confidence intervals (CIs)] were 1.27 (1.05-1.54) and 1.95 (1.57-2.42) among intermediate and high PM exposure groups compared to low PM exposure group. The relative risks of CAD were 40% (HR: 1.40, 95%CI: 1.18-1.66) and 133% (HR: 2.33, 95%CI: 1.94-2.79) higher among individuals at intermediate and high genetic risk than those at low genetic risk. Compared with individuals with both low genetic risk and low PM exposure, those with high genetic risk and high PM exposure had highest CAD risk, with HR of 4.37 (95%CI: 3.13-6.11). We observed significant multiplicative (P < 0.001) and additive interaction [relative excess risk due to interaction (95%CI): 2.75 (1.32-4.20); attributable proportion due to interaction (95%CI): 0.56 (0.42-0.70)] between genetic risk and PM exposure on CAD.
This study provided evidence that long-term PM exposure might increase CAD risk, especially among people at high genetic risk. Our findings highlighted the importance of taking strategies on air quality improvement to cardiovascular disease prevention.
尽管环境因素和遗传因素均与冠状动脉疾病(CAD)相关,但空气污染暴露与CAD之间的关联受遗传风险影响的程度尚不清楚。
纳入了从中国动脉粥样硬化性心血管疾病风险预测项目(China-PAR)招募的41149名参与者。基于540个基因变异构建CAD的遗传风险评分。采用1公里分辨率的卫星PM估计值评估长期PM暴露。我们使用分层Cox比例风险回归模型来检验PM暴露和遗传风险对CAD风险的影响,并进一步分析遗传易感性对PM暴露与CAD风险之间关联的修饰作用。
在中位随访13.01年期间,观察到1373例CAD事件。长期PM暴露显著增加CAD风险,与低PM暴露组相比,中、高PM暴露组的风险比(HRs)[95%置信区间(CIs)]分别为1.27(1.05 - 1.54)和1.95(1.57 - 2.42)。与低遗传风险个体相比,中、高遗传风险个体患CAD的相对风险分别高40%(HR:1.40,95%CI:1.18 - 1.66)和133%(HR:2.33,95%CI:1.94 - 2.79)。与低遗传风险且低PM暴露的个体相比,高遗传风险且高PM暴露的个体患CAD的风险最高,HR为4.37(95%CI:3.13 - 6.11)。我们观察到遗传风险和PM暴露对CAD存在显著的相乘交互作用(P < 0.001)和相加交互作用[交互作用导致的相对超额风险(95%CI):2.75(1.32 - 4.20);交互作用导致的归因比例(95%CI):0.56(0.42 - 0.70)]。
本研究提供了证据表明长期PM暴露可能增加CAD风险,尤其是在高遗传风险人群中。我们的研究结果强调了采取改善空气质量策略对预防心血管疾病的重要性。