住宅暴露于细颗粒物空气污染与扩张型心肌病的心脏表型受损有关

U. Tayal, D. Fecht, M. Chadeau, J. Gulliver, J. Ware, S. Cook, S. Prasad
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Long-term air pollution exposure estimates prior to the year of DCM diagnosis were assigned to each residential postcode centroid (on average 12 households). Annual average maps were available for NO2 concentrations in 2009 at 200m resolution and PM2.5 in 2010 at 100m resolution. Postcode centroids (x,y locations) were overlaid with each air pollution surface to obtain NO2 and PM2.5 estimates for each postcode and concentrations extrapolated to the year of diagnosis using information from the national air pollution monitoring network. Results From the total cohort of 716 DCM patients enrolled to the study, 678 patients had postcodes which could be assigned a geographical location and air pollutant estimates. The median PM2.5 concentration was 15.4 (14.3 – 16.3) μg/m3 and the median NO2 concentration was 32.4 (24.1 – 40.6) μg/m3. Higher residential exposure to PM2.5 and NO2 was associated with increased left ventricular mass in DCM patients (table 1). Higher residential exposure to NO2 was associated with reduced left ventricular ejection fraction (Table 1). There was no association between exposure to PM2.5 levels or NO2 levels and cardiovascular outcomes (NO2 Hazard ratio 0.99, 95% confidence intervals (CI) 0.98-1.01, p= 0.90; PM2.5 hazard ratio 1.0, 95% CI 0.89-1.25, p= 0.54). Conclusion Fine particulate matter air pollution has an adverse effect on cardiovascular phenotypes amongst patients with DCM suggesting air pollutants could be an environmental modifier of DCM. There was no apparent effect of fine particulate matter on major cardiovascular outcomes in this cohort. Future studies should explore whether air pollution contributes to DCM amongst at risk individuals. 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The biological basis for this is undefined, but environmental factors are plausible phenotypic modifiers. We sought to evaluate whether air pollution could be an important environmental modifier in DCM. Methods Prospectively recruited patients with DCM underwent advanced phenotyping by cardiac magnetic resonance. Patients were followed up for the primary composite end-point of cardiovascular mortality, major arrhythmic events and major heart failure events. Long-term air pollution exposure estimates prior to the year of DCM diagnosis were assigned to each residential postcode centroid (on average 12 households). Annual average maps were available for NO2 concentrations in 2009 at 200m resolution and PM2.5 in 2010 at 100m resolution. 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引用次数: 0

摘要

背景:在健康人群中,空气污染可能导致不利的心室重构。最近一项针对50万参与者的队列研究(UK Biobank)表明,居住暴露于空气动力学直径扩张型心肌病(DCM)的颗粒物具有显著的结构和功能表型异质性。生物学基础尚不明确,但环境因素是似是而非的表型修饰因子。我们试图评估空气污染是否可以成为DCM的重要环境调节剂。方法前瞻性招募DCM患者,通过心脏磁共振进行晚期表型分析。随访患者的主要复合终点为心血管死亡率、主要心律失常事件和主要心力衰竭事件。对每个住宅邮编质心(平均12户)分配了DCM诊断年份之前的长期空气污染暴露估计。2009年NO2浓度和2010年PM2.5浓度的年平均图分别为200米分辨率和100米分辨率。邮政编码质心(x,y位置)与每个空气污染表面叠加,以获得每个邮政编码的NO2和PM2.5估计值,并利用国家空气污染监测网络的信息外推到诊断年份的浓度。结果在纳入研究的716例DCM患者中,678例患者具有可分配地理位置和空气污染物估计值的邮政编码。PM2.5浓度中位数为15.4 (14.3 ~ 16.3)μg/m3, NO2浓度中位数为32.4 (24.1 ~ 40.6)μg/m3。较高的住宅暴露于PM2.5和NO2与DCM患者左心室质量增加相关(表1)。较高的住宅暴露于NO2与左心室射血分数降低相关(表1)。暴露于PM2.5水平或NO2水平与心血管结局之间没有关联(NO2风险比0.99,95%可信区间(CI) 0.98-1.01, p= 0.90;PM2.5风险比1.0,95% CI 0.89-1.25, p= 0.54)。结论空气细颗粒物污染对DCM患者心血管表型有不利影响,提示空气污染物可能是DCM的环境调节剂。在这个队列中,细颗粒物对主要心血管结局没有明显的影响。未来的研究应该探讨空气污染是否会导致高危人群的DCM。利益冲突无
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3 Residential exposure to fine particulate matter air pollution is associated with impaired cardiac phenotypes in dilated cardiomyopathy
Background Air pollution might contribute to adverse ventricular remodelling in healthy populations. A recent study on a cohort of 500,000 participants (UK Biobank) showed that residential exposure to particulate matter with aerodynamic diameter Dilated cardiomyopathy (DCM) has marked structural and functional phenotypic heterogeneity. The biological basis for this is undefined, but environmental factors are plausible phenotypic modifiers. We sought to evaluate whether air pollution could be an important environmental modifier in DCM. Methods Prospectively recruited patients with DCM underwent advanced phenotyping by cardiac magnetic resonance. Patients were followed up for the primary composite end-point of cardiovascular mortality, major arrhythmic events and major heart failure events. Long-term air pollution exposure estimates prior to the year of DCM diagnosis were assigned to each residential postcode centroid (on average 12 households). Annual average maps were available for NO2 concentrations in 2009 at 200m resolution and PM2.5 in 2010 at 100m resolution. Postcode centroids (x,y locations) were overlaid with each air pollution surface to obtain NO2 and PM2.5 estimates for each postcode and concentrations extrapolated to the year of diagnosis using information from the national air pollution monitoring network. Results From the total cohort of 716 DCM patients enrolled to the study, 678 patients had postcodes which could be assigned a geographical location and air pollutant estimates. The median PM2.5 concentration was 15.4 (14.3 – 16.3) μg/m3 and the median NO2 concentration was 32.4 (24.1 – 40.6) μg/m3. Higher residential exposure to PM2.5 and NO2 was associated with increased left ventricular mass in DCM patients (table 1). Higher residential exposure to NO2 was associated with reduced left ventricular ejection fraction (Table 1). There was no association between exposure to PM2.5 levels or NO2 levels and cardiovascular outcomes (NO2 Hazard ratio 0.99, 95% confidence intervals (CI) 0.98-1.01, p= 0.90; PM2.5 hazard ratio 1.0, 95% CI 0.89-1.25, p= 0.54). Conclusion Fine particulate matter air pollution has an adverse effect on cardiovascular phenotypes amongst patients with DCM suggesting air pollutants could be an environmental modifier of DCM. There was no apparent effect of fine particulate matter on major cardiovascular outcomes in this cohort. Future studies should explore whether air pollution contributes to DCM amongst at risk individuals. Conflict of Interest None
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