老年受试者多中心臭氧研究(MOSES):第2部分。个人和环境臭氧和其他污染物浓度对心血管和肺功能的影响。

D Q Rich, M W Frampton, J R Balmes, P A Bromberg, M Arjomandi, M J Hazucha, S W Thurston, N E Alexis, P Ganz, W Zareba, P Koutrakis, K Thevenet-Morrison
{"title":"老年受试者多中心臭氧研究(MOSES):第2部分。个人和环境臭氧和其他污染物浓度对心血管和肺功能的影响。","authors":"D Q Rich,&nbsp;M W Frampton,&nbsp;J R Balmes,&nbsp;P A Bromberg,&nbsp;M Arjomandi,&nbsp;M J Hazucha,&nbsp;S W Thurston,&nbsp;N E Alexis,&nbsp;P Ganz,&nbsp;W Zareba,&nbsp;P Koutrakis,&nbsp;K Thevenet-Morrison","doi":"","DOIUrl":null,"url":null,"abstract":"<p><strong>Introduction: </strong>The Multicenter Ozone Study of oldEr Subjects (MOSES) was a multi-center study evaluating whether short-term controlled exposure of older, healthy individuals to low levels of ozone (O<sub>3</sub>) induced acute changes in cardiovascular biomarkers. In MOSES Part 1 (MOSES 1), controlled O<sub>3</sub> exposure caused concentration-related reductions in lung function with evidence of airway inflammation and injury, but without convincing evidence of effects on cardiovascular function. However, subjects' prior exposures to indoor and outdoor air pollution in the few hours and days before each MOSES controlled O<sub>3</sub> exposure may have independently affected the study biomarkers and/or modified biomarker responses to the MOSES controlled O<sub>3</sub> exposures.</p><p><strong>Methods: </strong>MOSES 1 was conducted at three clinical centers (University of California San Francisco, University of North Carolina, and University of Rochester Medical Center) and included healthy volunteers 55 to 70 years of age. Consented participants who successfully completed the screening and training sessions were enrolled in the study. All three clinical centers adhered to common standard operating procedures and used common tracking and data forms. Each subject was scheduled to participate in a total of 11 visits: screening visit, training visit, and three sets of exposure visits consisting of the pre-exposure day, the exposure day, and the post-exposure day. After completing the pre-exposure day, subjects spent the night in a nearby hotel. On exposure days, the subjects were exposed for 3 hours in random order to 0 ppb O<sub>3</sub> (clean air), 70 ppb O<sub>3</sub>, and 120 ppm O<sub>3</sub>. During the exposure period the subjects alternated between 15 minutes of moderate exercise and 15 minutes of rest. A suite of cardiovascular and pulmonary endpoints was measured on the day before, the day of, and up to 22 hours after each exposure.</p><p><p>In MOSES Part 2 (MOSES 2), we used a longitudinal panel study design, cardiopulmonary biomarker data from MOSES 1, passive cumulative personal exposure samples (PES) of O<sub>3</sub> and nitrogen dioxide (NO<sub>2</sub>) in the 72 hours before the pre-exposure visit, and hourly ambient air pollution and weather measurements in the 96 hours before the pre-exposure visit. We used mixed-effects linear regression and evaluated whether PES O<sub>3</sub> and NO<sub>2</sub> and these ambient pollutant concentrations in the 96 hours before the pre-exposure visit confounded the MOSES 1 controlled O<sub>3</sub> exposure effects on the pre- to post-exposure biomarker changes (Aim 1), whether they modified these pre- to post-exposure biomarker responses to the controlled O<sub>3</sub> exposures (Aim 2), whether they were associated with changes in biomarkers measured at the pre-exposure visit or morning of the exposure session (Aim 3), and whether they were associated with differences in the pre- to post-exposure biomarker changes independently of the controlled O<sub>3</sub> exposures (Aim 4).</p><p><strong>Results: </strong>Ambient pollutant concentrations at each site were low and were regularly below the National Ambient Air Quality Standard levels. In Aim 1, the controlled O<sub>3</sub> exposure effects on the pre- to post-exposure biomarker differences were little changed when PES or ambient pollutant concentrations in the previous 96 hours were included in the model, suggesting these were not confounders of the controlled O<sub>3</sub> exposure/biomarker difference associations. In Aim 2, effects of MOSES controlled O<sub>3</sub> exposures on forced expiratory volume in 1 second (FEV<sub>1</sub>) and forced vital capacity (FVC) were modified by ambient NO<sub>2</sub> and carbon monoxide (CO), and PES NO<sub>2</sub>, with reductions in FEV<sub>1</sub> and FVC observed only when these concentrations were \"Medium\" or \"High\" in the 72 hours before the pre-exposure visit. There was no such effect modification of the effect of controlled O<sub>3</sub> exposure on any other cardiopulmonary biomarker.</p><p><p>As hypothesized for Aim 3, increased ambient O<sub>3</sub> concentrations were associated with decreased pre-exposure heart rate variability (HRV). For example, high frequency (HF) HRV decreased in association with increased ambient O<sub>3</sub> concentrations in the 96 hours before the pre-exposure visit (-0.460 ln[ms<sup>2</sup>]; 95% CI, -0.743 to -0.177 for each 10.35-ppb increase in O<sub>3</sub>; <i>P</i> = 0.002). However, in Aim 4 these increases in ambient O<sub>3</sub> were also associated with increases in HF and low frequency (LF) HRV from pre- to post-exposure, likely reflecting a \"recovery\" of HRV during the MOSES O<sub>3</sub> exposure sessions. Similar patterns across Aims 3 and 4 were observed for LF (the other primary HRV marker), and standard deviation of normal-to-normal sinus beat intervals (SDNN) and root mean square of successive differences in normal-to-normal sinus beat intervals (RMSSD) (secondary HRV markers).</p><p><p>Similar Aim 3 and Aim 4 patterns were observed for FEV<sub>1</sub> and FVC in association with increases in ambient PM with an aerodynamic diameter ≤ 2.5 μm (PM<sub>2.5</sub>), CO, and NO<sub>2</sub> in the 96 hours before the pre-exposure visit. For Aim 3, small decreases in pre-exposure FEV<sub>1</sub> were significantly associated with interquartile range (IQR) increases in PM<sub>2.5</sub> concentrations in the 1 hour before the pre-exposure visit (-0.022 L; 95% CI, -0.037 to -0.006; <i>P</i> = 0.007), CO in the 3 hours before the pre-exposure visit (-0.046 L; 95% CI, -0.076 to -0.016; <i>P</i> = 0.003), and NO<sub>2</sub> in the 72 hours before the pre-exposure visit (-0.030 L; 95% CI, -0.052 to -0.008; <i>P</i> = 0.007). However, FEV<sub>1</sub> was not associated with ambient O<sub>3</sub> or sulfur dioxide (SO<sub>2</sub>), or PES O<sub>3</sub> or NO<sub>2</sub> (Aim 3). For Aim 4, increased FEV<sub>1</sub> across the exposure session (post-exposure minus pre-exposure) was marginally significantly associated with each 4.1-ppb increase in PES O<sub>3</sub> concentration (0.010 L; 95% CI, 0.004 to 0.026; <i>P</i> = 0.010), as well as ambient PM<sub>2.5</sub> and CO at all lag times. FVC showed similar associations, with patterns of decreased pre-exposure FVC associated with increased PM<sub>2.5</sub>, CO, and NO<sub>2</sub> at most lag times, and increased FVC across the exposure session also associated with increased concentrations of the same pollutants, reflecting a similar recovery. However, increased pollutant concentrations were not associated with adverse changes in pre-exposure levels or pre- to post-exposure changes in biomarkers of cardiac repolarization, ST segment, vascular function, nitrotyrosine as a measure of oxidative stress, prothrombotic state, systemic inflammation, lung injury, or sputum polymorphonuclear leukocyte (PMN) percentage as a measure of airway inflammation.</p><p><strong>Conclusions: </strong>Our previous MOSES 1 findings of controlled O<sub>3</sub> exposure effects on pulmonary function, but not on any cardiovascular biomarker, were not confounded by ambient or personal O<sub>3</sub> or other pollutant exposures in the 96 and 72 hours before the pre-exposure visit. Further, these MOSES 1 O<sub>3</sub> effects were generally not modified, blunted, or lessened by these same ambient and personal pollutant exposures. However, the reductions in markers of pulmonary function by the MOSES 1 controlled O<sub>3</sub> exposure were modified by ambient NO<sub>2</sub> and CO, and PES NO<sub>2</sub>, with reductions observed only when these pollutant concentrations were elevated in the few hours and days before the pre-exposure visit. Increased ambient O<sub>3</sub> concentrations were associated with reduced HRV, with \"recovery\" during exposure visits. Increased ambient PM<sub>2.5</sub>, NO<sub>2</sub>, and CO were associated with reduced pulmonary function, independent of the MOSES-controlled O<sub>3</sub> exposures. Increased pollutant concentrations were not associated with pre-exposure or pre- to post-exposure changes in other cardiopulmonary biomarkers. Future controlled exposure studies should consider the effect of ambient pollutants on pre-exposure biomarker levels and whether ambient pollutants modify any health response to a controlled pollutant exposure.</p>","PeriodicalId":74687,"journal":{"name":"Research report (Health Effects Institute)","volume":" 192, Pt 2","pages":"1-90"},"PeriodicalIF":0.0000,"publicationDate":"2020-03-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7325421/pdf/hei-2020-192-p2.pdf","citationCount":"0","resultStr":"{\"title\":\"Multicenter Ozone Study in oldEr Subjects (MOSES): Part 2. 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However, subjects' prior exposures to indoor and outdoor air pollution in the few hours and days before each MOSES controlled O<sub>3</sub> exposure may have independently affected the study biomarkers and/or modified biomarker responses to the MOSES controlled O<sub>3</sub> exposures.</p><p><strong>Methods: </strong>MOSES 1 was conducted at three clinical centers (University of California San Francisco, University of North Carolina, and University of Rochester Medical Center) and included healthy volunteers 55 to 70 years of age. Consented participants who successfully completed the screening and training sessions were enrolled in the study. All three clinical centers adhered to common standard operating procedures and used common tracking and data forms. Each subject was scheduled to participate in a total of 11 visits: screening visit, training visit, and three sets of exposure visits consisting of the pre-exposure day, the exposure day, and the post-exposure day. After completing the pre-exposure day, subjects spent the night in a nearby hotel. On exposure days, the subjects were exposed for 3 hours in random order to 0 ppb O<sub>3</sub> (clean air), 70 ppb O<sub>3</sub>, and 120 ppm O<sub>3</sub>. During the exposure period the subjects alternated between 15 minutes of moderate exercise and 15 minutes of rest. A suite of cardiovascular and pulmonary endpoints was measured on the day before, the day of, and up to 22 hours after each exposure.</p><p><p>In MOSES Part 2 (MOSES 2), we used a longitudinal panel study design, cardiopulmonary biomarker data from MOSES 1, passive cumulative personal exposure samples (PES) of O<sub>3</sub> and nitrogen dioxide (NO<sub>2</sub>) in the 72 hours before the pre-exposure visit, and hourly ambient air pollution and weather measurements in the 96 hours before the pre-exposure visit. We used mixed-effects linear regression and evaluated whether PES O<sub>3</sub> and NO<sub>2</sub> and these ambient pollutant concentrations in the 96 hours before the pre-exposure visit confounded the MOSES 1 controlled O<sub>3</sub> exposure effects on the pre- to post-exposure biomarker changes (Aim 1), whether they modified these pre- to post-exposure biomarker responses to the controlled O<sub>3</sub> exposures (Aim 2), whether they were associated with changes in biomarkers measured at the pre-exposure visit or morning of the exposure session (Aim 3), and whether they were associated with differences in the pre- to post-exposure biomarker changes independently of the controlled O<sub>3</sub> exposures (Aim 4).</p><p><strong>Results: </strong>Ambient pollutant concentrations at each site were low and were regularly below the National Ambient Air Quality Standard levels. In Aim 1, the controlled O<sub>3</sub> exposure effects on the pre- to post-exposure biomarker differences were little changed when PES or ambient pollutant concentrations in the previous 96 hours were included in the model, suggesting these were not confounders of the controlled O<sub>3</sub> exposure/biomarker difference associations. In Aim 2, effects of MOSES controlled O<sub>3</sub> exposures on forced expiratory volume in 1 second (FEV<sub>1</sub>) and forced vital capacity (FVC) were modified by ambient NO<sub>2</sub> and carbon monoxide (CO), and PES NO<sub>2</sub>, with reductions in FEV<sub>1</sub> and FVC observed only when these concentrations were \\\"Medium\\\" or \\\"High\\\" in the 72 hours before the pre-exposure visit. There was no such effect modification of the effect of controlled O<sub>3</sub> exposure on any other cardiopulmonary biomarker.</p><p><p>As hypothesized for Aim 3, increased ambient O<sub>3</sub> concentrations were associated with decreased pre-exposure heart rate variability (HRV). For example, high frequency (HF) HRV decreased in association with increased ambient O<sub>3</sub> concentrations in the 96 hours before the pre-exposure visit (-0.460 ln[ms<sup>2</sup>]; 95% CI, -0.743 to -0.177 for each 10.35-ppb increase in O<sub>3</sub>; <i>P</i> = 0.002). However, in Aim 4 these increases in ambient O<sub>3</sub> were also associated with increases in HF and low frequency (LF) HRV from pre- to post-exposure, likely reflecting a \\\"recovery\\\" of HRV during the MOSES O<sub>3</sub> exposure sessions. Similar patterns across Aims 3 and 4 were observed for LF (the other primary HRV marker), and standard deviation of normal-to-normal sinus beat intervals (SDNN) and root mean square of successive differences in normal-to-normal sinus beat intervals (RMSSD) (secondary HRV markers).</p><p><p>Similar Aim 3 and Aim 4 patterns were observed for FEV<sub>1</sub> and FVC in association with increases in ambient PM with an aerodynamic diameter ≤ 2.5 μm (PM<sub>2.5</sub>), CO, and NO<sub>2</sub> in the 96 hours before the pre-exposure visit. For Aim 3, small decreases in pre-exposure FEV<sub>1</sub> were significantly associated with interquartile range (IQR) increases in PM<sub>2.5</sub> concentrations in the 1 hour before the pre-exposure visit (-0.022 L; 95% CI, -0.037 to -0.006; <i>P</i> = 0.007), CO in the 3 hours before the pre-exposure visit (-0.046 L; 95% CI, -0.076 to -0.016; <i>P</i> = 0.003), and NO<sub>2</sub> in the 72 hours before the pre-exposure visit (-0.030 L; 95% CI, -0.052 to -0.008; <i>P</i> = 0.007). However, FEV<sub>1</sub> was not associated with ambient O<sub>3</sub> or sulfur dioxide (SO<sub>2</sub>), or PES O<sub>3</sub> or NO<sub>2</sub> (Aim 3). For Aim 4, increased FEV<sub>1</sub> across the exposure session (post-exposure minus pre-exposure) was marginally significantly associated with each 4.1-ppb increase in PES O<sub>3</sub> concentration (0.010 L; 95% CI, 0.004 to 0.026; <i>P</i> = 0.010), as well as ambient PM<sub>2.5</sub> and CO at all lag times. FVC showed similar associations, with patterns of decreased pre-exposure FVC associated with increased PM<sub>2.5</sub>, CO, and NO<sub>2</sub> at most lag times, and increased FVC across the exposure session also associated with increased concentrations of the same pollutants, reflecting a similar recovery. However, increased pollutant concentrations were not associated with adverse changes in pre-exposure levels or pre- to post-exposure changes in biomarkers of cardiac repolarization, ST segment, vascular function, nitrotyrosine as a measure of oxidative stress, prothrombotic state, systemic inflammation, lung injury, or sputum polymorphonuclear leukocyte (PMN) percentage as a measure of airway inflammation.</p><p><strong>Conclusions: </strong>Our previous MOSES 1 findings of controlled O<sub>3</sub> exposure effects on pulmonary function, but not on any cardiovascular biomarker, were not confounded by ambient or personal O<sub>3</sub> or other pollutant exposures in the 96 and 72 hours before the pre-exposure visit. Further, these MOSES 1 O<sub>3</sub> effects were generally not modified, blunted, or lessened by these same ambient and personal pollutant exposures. 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引用次数: 0

摘要

老年受试者多中心臭氧研究(MOSES)是一项多中心研究,评估老年人健康个体短期受控暴露于低水平臭氧(O3)是否会引起心血管生物标志物的急性变化。在MOSES Part 1 (MOSES 1)中,受控的O3暴露引起了与浓度相关的肺功能降低,有气道炎症和损伤的证据,但没有令人信服的证据表明对心血管功能有影响。然而,受试者在每次摩西控制臭氧暴露前几小时和几天内暴露于室内和室外空气污染可能会独立影响研究生物标志物和/或修饰生物标志物对摩西控制臭氧暴露的反应。方法:MOSES 1在三个临床中心(加州大学旧金山分校、北卡罗来纳大学和罗切斯特大学医学中心)进行,包括55至70岁的健康志愿者。成功完成筛选和培训课程的同意参与者被纳入研究。所有三个临床中心都遵守共同的标准操作程序,并使用共同的跟踪和数据表格。每位受试者计划参加共11次访视:筛查访视、培训访视和三组暴露访视,包括暴露前、暴露日和暴露后。在完成曝光前的一天后,被试在附近的一家酒店过夜。在暴露日,受试者按随机顺序暴露于0 ppb O3(清洁空气)、70 ppb O3和120 ppm O3中3小时。在暴露期间,受试者交替进行15分钟的适度运动和15分钟的休息。在每次暴露的前一天、当天和22小时后测量一组心血管和肺终点。在MOSES Part 2 (MOSES 2)中,我们采用纵向面板研究设计,MOSES 1的心肺生物标志物数据,暴露前访问前72小时的臭氧和二氧化氮(NO2)被动累积个人暴露样本(PES),以及暴露前访问前96小时的每小时环境空气污染和天气测量。我们使用混合效应线性回归,评估了暴露前访问前96小时内PES O3和NO2以及这些环境污染物浓度是否混淆了MOSES 1控制的O3暴露对暴露前后生物标志物变化的影响(目的1),以及它们是否修改了这些暴露前后生物标志物对受控O3暴露的反应(目的2)。它们是否与暴露前访问或暴露时段上午测量的生物标志物变化有关(目标3),以及它们是否与独立于受控臭氧暴露的暴露前后生物标志物变化的差异有关(目标4)。结果:每个站点的环境污染物浓度都很低,并且经常低于国家环境空气质量标准水平。在Aim 1中,当将前96小时的PES或环境污染物浓度纳入模型时,受控的臭氧暴露对暴露前后生物标志物差异的影响几乎没有变化,这表明这些不是受控的臭氧暴露/生物标志物差异关联的混杂因素。在Aim 2中,MOSES控制的O3暴露对1秒用力呼气量(FEV1)和用力肺活量(FVC)的影响被环境NO2和一氧化碳(CO)以及PES NO2所改变,只有在暴露前访问前72小时内这些浓度为“中等”或“高”时才会观察到FEV1和FVC的降低。控制臭氧暴露对任何其他心肺生物标志物的影响没有这种影响的改变。正如Aim 3的假设,环境O3浓度的增加与暴露前心率变异性(HRV)的降低有关。例如,暴露前访问前96小时内,高频(HF) HRV随着环境O3浓度的增加而下降(-0.460 ln[ms2];O3浓度每增加10.35 ppb, 95% CI为-0.743 ~ -0.177;P = 0.002)。然而,在Aim 4中,这些环境O3的增加也与暴露前后HF和低频(LF) HRV的增加有关,可能反映了在MOSES O3暴露期间HRV的“恢复”。在目标3和目标4中,观察到LF(另一个主要HRV指标)、正常至正常窦性搏动间隔(SDNN)的标准差和正常至正常窦性搏动间隔(RMSSD)连续差异的均方根(次要HRV指标)的相似模式。在暴露前的96小时内,FEV1和FVC与空气动力学直径≤2.5 μm的PM (PM2.5)、CO和NO2的增加有相似的Aim 3和Aim 4模式。 对于Aim 3,暴露前FEV1的小幅下降与暴露前1小时PM2.5浓度的四分位数范围(IQR)增加显著相关(-0.022 L;95% CI, -0.037 ~ -0.006;P = 0.007),暴露前访视前3小时CO (-0.046 L;95% CI, -0.076 ~ -0.016;P = 0.003),暴露前访问前72小时NO2 (-0.030 L;95% CI, -0.052 ~ -0.008;P = 0.007)。然而,FEV1与环境O3或二氧化硫(SO2)或PES O3或NO2 (Aim 3)无关。对于Aim 4,在暴露过程中(暴露后减去暴露前)FEV1的增加与PES O3浓度每增加4.1 ppb (0.010 L;95% CI, 0.004 ~ 0.026;P = 0.010),以及所有滞后时间的环境PM2.5和CO。植被覆盖度也表现出类似的关联,暴露前植被覆盖度的减少与PM2.5、CO和NO2的增加在大多数滞后时间相关,而暴露过程中植被覆盖度的增加也与相同污染物浓度的增加相关,反映出类似的恢复。然而,污染物浓度的增加与暴露前或暴露后心脏复极、ST段、血管功能、衡量氧化应激的硝基酪氨酸、血栓形成前状态、全身炎症、肺损伤或衡量气道炎症的痰多形核白细胞(PMN)百分比的生物标志物的不利变化无关。结论:我们之前的MOSES 1研究发现,可控的臭氧暴露对肺功能有影响,但对任何心血管生物标志物没有影响,这与暴露前访问前96和72小时的环境或个人臭氧或其他污染物暴露不一致。此外,这些moso3效应通常不会被这些相同的环境和个人污染物暴露所改变、减弱或减轻。然而,mos1控制的O3暴露导致的肺功能标志物的减少被环境NO2和CO以及PES NO2所改变,只有在暴露前访问前几小时和几天内这些污染物浓度升高时才会观察到减少。环境O3浓度的增加与HRV的降低有关,并在接触期间“恢复”。增加的环境PM2.5、NO2和CO与肺功能降低有关,与moses控制的O3暴露无关。污染物浓度的增加与暴露前或暴露前后其他心肺生物标志物的变化无关。未来的受控暴露研究应考虑环境污染物对暴露前生物标志物水平的影响,以及环境污染物是否会改变对受控污染物暴露的任何健康反应。
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Multicenter Ozone Study in oldEr Subjects (MOSES): Part 2. Effects of Personal and Ambient Concentrations of Ozone and Other Pollutants on Cardiovascular and Pulmonary Function.

Introduction: The Multicenter Ozone Study of oldEr Subjects (MOSES) was a multi-center study evaluating whether short-term controlled exposure of older, healthy individuals to low levels of ozone (O3) induced acute changes in cardiovascular biomarkers. In MOSES Part 1 (MOSES 1), controlled O3 exposure caused concentration-related reductions in lung function with evidence of airway inflammation and injury, but without convincing evidence of effects on cardiovascular function. However, subjects' prior exposures to indoor and outdoor air pollution in the few hours and days before each MOSES controlled O3 exposure may have independently affected the study biomarkers and/or modified biomarker responses to the MOSES controlled O3 exposures.

Methods: MOSES 1 was conducted at three clinical centers (University of California San Francisco, University of North Carolina, and University of Rochester Medical Center) and included healthy volunteers 55 to 70 years of age. Consented participants who successfully completed the screening and training sessions were enrolled in the study. All three clinical centers adhered to common standard operating procedures and used common tracking and data forms. Each subject was scheduled to participate in a total of 11 visits: screening visit, training visit, and three sets of exposure visits consisting of the pre-exposure day, the exposure day, and the post-exposure day. After completing the pre-exposure day, subjects spent the night in a nearby hotel. On exposure days, the subjects were exposed for 3 hours in random order to 0 ppb O3 (clean air), 70 ppb O3, and 120 ppm O3. During the exposure period the subjects alternated between 15 minutes of moderate exercise and 15 minutes of rest. A suite of cardiovascular and pulmonary endpoints was measured on the day before, the day of, and up to 22 hours after each exposure.

In MOSES Part 2 (MOSES 2), we used a longitudinal panel study design, cardiopulmonary biomarker data from MOSES 1, passive cumulative personal exposure samples (PES) of O3 and nitrogen dioxide (NO2) in the 72 hours before the pre-exposure visit, and hourly ambient air pollution and weather measurements in the 96 hours before the pre-exposure visit. We used mixed-effects linear regression and evaluated whether PES O3 and NO2 and these ambient pollutant concentrations in the 96 hours before the pre-exposure visit confounded the MOSES 1 controlled O3 exposure effects on the pre- to post-exposure biomarker changes (Aim 1), whether they modified these pre- to post-exposure biomarker responses to the controlled O3 exposures (Aim 2), whether they were associated with changes in biomarkers measured at the pre-exposure visit or morning of the exposure session (Aim 3), and whether they were associated with differences in the pre- to post-exposure biomarker changes independently of the controlled O3 exposures (Aim 4).

Results: Ambient pollutant concentrations at each site were low and were regularly below the National Ambient Air Quality Standard levels. In Aim 1, the controlled O3 exposure effects on the pre- to post-exposure biomarker differences were little changed when PES or ambient pollutant concentrations in the previous 96 hours were included in the model, suggesting these were not confounders of the controlled O3 exposure/biomarker difference associations. In Aim 2, effects of MOSES controlled O3 exposures on forced expiratory volume in 1 second (FEV1) and forced vital capacity (FVC) were modified by ambient NO2 and carbon monoxide (CO), and PES NO2, with reductions in FEV1 and FVC observed only when these concentrations were "Medium" or "High" in the 72 hours before the pre-exposure visit. There was no such effect modification of the effect of controlled O3 exposure on any other cardiopulmonary biomarker.

As hypothesized for Aim 3, increased ambient O3 concentrations were associated with decreased pre-exposure heart rate variability (HRV). For example, high frequency (HF) HRV decreased in association with increased ambient O3 concentrations in the 96 hours before the pre-exposure visit (-0.460 ln[ms2]; 95% CI, -0.743 to -0.177 for each 10.35-ppb increase in O3; P = 0.002). However, in Aim 4 these increases in ambient O3 were also associated with increases in HF and low frequency (LF) HRV from pre- to post-exposure, likely reflecting a "recovery" of HRV during the MOSES O3 exposure sessions. Similar patterns across Aims 3 and 4 were observed for LF (the other primary HRV marker), and standard deviation of normal-to-normal sinus beat intervals (SDNN) and root mean square of successive differences in normal-to-normal sinus beat intervals (RMSSD) (secondary HRV markers).

Similar Aim 3 and Aim 4 patterns were observed for FEV1 and FVC in association with increases in ambient PM with an aerodynamic diameter ≤ 2.5 μm (PM2.5), CO, and NO2 in the 96 hours before the pre-exposure visit. For Aim 3, small decreases in pre-exposure FEV1 were significantly associated with interquartile range (IQR) increases in PM2.5 concentrations in the 1 hour before the pre-exposure visit (-0.022 L; 95% CI, -0.037 to -0.006; P = 0.007), CO in the 3 hours before the pre-exposure visit (-0.046 L; 95% CI, -0.076 to -0.016; P = 0.003), and NO2 in the 72 hours before the pre-exposure visit (-0.030 L; 95% CI, -0.052 to -0.008; P = 0.007). However, FEV1 was not associated with ambient O3 or sulfur dioxide (SO2), or PES O3 or NO2 (Aim 3). For Aim 4, increased FEV1 across the exposure session (post-exposure minus pre-exposure) was marginally significantly associated with each 4.1-ppb increase in PES O3 concentration (0.010 L; 95% CI, 0.004 to 0.026; P = 0.010), as well as ambient PM2.5 and CO at all lag times. FVC showed similar associations, with patterns of decreased pre-exposure FVC associated with increased PM2.5, CO, and NO2 at most lag times, and increased FVC across the exposure session also associated with increased concentrations of the same pollutants, reflecting a similar recovery. However, increased pollutant concentrations were not associated with adverse changes in pre-exposure levels or pre- to post-exposure changes in biomarkers of cardiac repolarization, ST segment, vascular function, nitrotyrosine as a measure of oxidative stress, prothrombotic state, systemic inflammation, lung injury, or sputum polymorphonuclear leukocyte (PMN) percentage as a measure of airway inflammation.

Conclusions: Our previous MOSES 1 findings of controlled O3 exposure effects on pulmonary function, but not on any cardiovascular biomarker, were not confounded by ambient or personal O3 or other pollutant exposures in the 96 and 72 hours before the pre-exposure visit. Further, these MOSES 1 O3 effects were generally not modified, blunted, or lessened by these same ambient and personal pollutant exposures. However, the reductions in markers of pulmonary function by the MOSES 1 controlled O3 exposure were modified by ambient NO2 and CO, and PES NO2, with reductions observed only when these pollutant concentrations were elevated in the few hours and days before the pre-exposure visit. Increased ambient O3 concentrations were associated with reduced HRV, with "recovery" during exposure visits. Increased ambient PM2.5, NO2, and CO were associated with reduced pulmonary function, independent of the MOSES-controlled O3 exposures. Increased pollutant concentrations were not associated with pre-exposure or pre- to post-exposure changes in other cardiopulmonary biomarkers. Future controlled exposure studies should consider the effect of ambient pollutants on pre-exposure biomarker levels and whether ambient pollutants modify any health response to a controlled pollutant exposure.

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