Ministry of Education Key Laboratory of Environment and Health, and State Key Laboratory of Environmental Health (Incubating), School of Public Health, Tongji Medical College, Huazhong University of Science and Technology, No.13 Hangkong Road, Wuhan, 430030, China; Department of Maternal and Child Health, School of Public Health, Tongji Medical College, Huazhong University of Science and Technology, No.13 Hangkong Road, Wuhan, 430030, China.
Ministry of Education Key Laboratory of Environment and Health, and State Key Laboratory of Environmental Health (Incubating), School of Public Health, Tongji Medical College, Huazhong University of Science and Technology, No.13 Hangkong Road, Wuhan, 430030, China; Department of Maternal and Child Health, School of Public Health, Tongji Medical College, Huazhong University of Science and Technology, No.13 Hangkong Road, Wuhan, 430030, China.
Psychiatry Res. 2023 Sep;327:115396. doi: 10.1016/j.psychres.2023.115396. Epub 2023 Aug 3.
There is mounting recent evidence showing that air pollution exposure may be related to the risk of mental health, yet the association between long-term exposure to air pollution and the risk of incident bipolar disorder (BD) remains unclear. Thus we aim to identify associations between air pollution and the incidence of BD in a prospective population-based cohort. In total, 482,726 participants who were free of BD from the UK Biobank were included in this prospective study. We applied time-varying Cox proportional hazards models, accounting for relevant confounders, and used annual-year moving averages of air pollution as time-varying exposures. The genetic risk for BD was categorized into three categories (low, intermediate, and high) according to the tertiles of polygenic risk score. During a median of 10.79-year follow-up, 923 incident BD events were recorded. Long-term exposures to PM, PM, NO, and NO were associated with increased BD risk. Estimated HRs (95% CIs) for each interquartile range increase in PM, PM, NO, and NO concentrations were 1.31 (1.18-1.45), 1.19 (1.09-1.31), 1.19 (1.08-1.30), and 1.16 (1.07-1.26), respectively. Associations were still observed and even stronger at pollutant concentrations lower than WHO air quality guideline. In subgroup analysis stratified by genetic risk, we observed consistent associations between all pollutants and BD risk in intermediate and high genetic risk groups, but not in low genetic risk group. For example, the HRs (95% CIs) for PM were 1.00 (0.94-1.53), 1.30 (1.06-1.59), and 1.34 (1.16-1.54) in low, intermediate, and high genetic groups, respectively. In conclusion, long-term exposure to air pollution was significantly associated with an elevated risk of BD. Associations of air pollution with BD occurred only within intermediate and high genetic risk categories and were even stronger at the pollutants levels below WHO air quality guidelines. These findings could help inform policy makers regarding ambient air quality standards and BD management.
越来越多的证据表明,空气污染暴露可能与心理健康风险有关,但长期暴露于空气污染与双相情感障碍(BD)发病风险之间的关联尚不清楚。因此,我们旨在确定在一个前瞻性的基于人群的队列中,空气污染与 BD 发病之间的关联。在这项前瞻性研究中,共纳入了来自英国生物库的 482726 名无 BD 的参与者。我们应用了时变 Cox 比例风险模型,考虑了相关的混杂因素,并使用空气污染的年度年移动平均值作为时变暴露。BD 的遗传风险根据多基因风险评分的三分位数分为低、中、高三个类别。在中位 10.79 年的随访期间,记录了 923 例新发 BD 事件。长期暴露于 PM、PM、NO 和 NO 与 BD 风险增加相关。PM、PM、NO 和 NO 浓度每增加一个四分位间距,估计的 HR(95%CI)分别为 1.31(1.18-1.45)、1.19(1.09-1.31)、1.19(1.08-1.30)和 1.16(1.07-1.26)。在低于世界卫生组织空气质量指南的污染物浓度下,仍观察到关联,且关联更强。在按遗传风险分层的亚组分析中,我们观察到所有污染物与中、高遗传风险组的 BD 风险之间存在一致的关联,但在低遗传风险组中没有关联。例如,在低、中、高遗传风险组中,PM 的 HR(95%CI)分别为 1.00(0.94-1.53)、1.30(1.06-1.59)和 1.34(1.16-1.54)。总之,长期暴露于空气污染与 BD 风险增加显著相关。空气污染与 BD 之间的关联仅发生在中、高遗传风险类别中,在低于世界卫生组织空气质量指南的污染物水平下,关联更强。这些发现可能有助于决策者了解环境空气质量标准和 BD 管理。