估计空气质量法规对健康长期影响的因果推理方法。

Corwin Matthew Zigler, Chanmin Kim, Christine Choirat, John Barrett Hansen, Yun Wang, Lauren Hund, Jonathan Samet, Gary King, Francesca Dominici
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引用次数: 0

摘要

导言:围绕空气质量管理的监管和政策环境需要新的流行病学证据。空气污染流行病学通常为以前的政策提供污染与健康结果之间暴露-反应关系的估计,而新类型的证据可以为当前关于空气质量法规对健康的实际影响的辩论提供信息。直接评估具体的监管策略不同于评估暴露-反应关系,并对其进行补充;更加重视评估定义明确的监管干预措施的有效性,将加强支持政策决定的证据。本报告的目的是提供新的分析视角和统计方法,我们称之为“直接”问责制评估具体空气质量监管干预措施的有效性。为此,我们强化了HEI问责工作组(2003年)通过讨论、发展和部署从观测数据中得出因果推论的统计方法最初提出的围绕问责评估的许多区别。这里提出的方法和分析是统一的,它们的重点是将问责制评估锚定在对明确定义的行动或干预措施的因果后果的估计上。这些分析观点是在两个直接问责案例研究的背景下讨论的,这些案例研究涉及所谓问责链中的四个不同环节,即从干预到预期结果的一系列相关事件(见前言;HEI问责工作组2003)。方法:本报告中描述的统计方法包括从观测数据中得出因果推论的既定方法和评估因果责任的新开发方法。我们加强了直接评估具体政策有效性的研究与估计污染与健康之间暴露-反应关系的研究之间的分析区别。我们强调因果推理的潜在结果范式如何通过更直接的证据来证明复杂的监管干预对污染和健康结果的影响程度,从而提升政策辩论。我们还概述了潜在结果的观点,并将其作为一种将观察性研究框架化为近似随机实验的手段。我们新开发的评估因果责任的方法利用倾向得分、主分层、因果中介分析、空间层次模型和贝叶斯估计。第一个案例研究利用生活在美国西部的大约400万医疗保险受益人的健康结果,根据1987年国家环境空气质量标准(NAAQS),估计空气动力学直径≤10 μm (PM10*)被指定为不达标区域的因果健康影响。第二个案例研究的重点是开发和测试我们新的、先进的多污染物责任评估方法,通过检查燃煤电厂的二氧化硫(SO2)洗涤器对二氧化硫、氮氧化物(NO(x))和二氧化碳(CO2)排放的因果影响程度,以及减排在多大程度上调节了洗涤器对PM2.5环境浓度的因果影响。这两个案例研究都基于我们对环境空气质量监测、天气、人口统计、医疗保险住院和死亡率结果、发电厂发电机组(egu)持续排放监测以及各种监管控制干预措施等国家相关数据的汇编。由此产生的数据库具有前所未有的准确性和粒度,可用于开展本报告中提出的各种问责性评估。我们工作的一个关键组成部分是创建工具来帮助分发我们的链接数据库,并促进可重复的研究。结果:在第一个案例研究中,我们重点阐述了直接问责评估的因果推理视角的最基本特征。结果表明,1990年至1995年期间,在被指定为PM10未达标地区,与没有指定的地区相比,全因医疗保险死亡率和呼吸相关住院率都有所下降。在第二个案例研究中,研究了发电厂的排放,并说明了我们新开发的统计方法,结果表明,二氧化硫洗涤器的存在会导致环境PM2.5的减少,而这种减少几乎完全是通过二氧化硫排放的因果减少来调节的。研究结果是根据洗涤器、发电厂排放和PM2.5之间有充分记录的关系来解释的。 结论:通过将问责制研究置于潜在结果框架中,并将我们的新方法应用于我们收集的国家数据集,我们能够提供长期、大规模空气质量法规对健康影响的额外可靠证据。这一关于明确界定的行动的因果效应的额外、严格的证据增强了现有的研究体系,并确保最高级别的流行病学证据将继续支持监管政策。最终,我们的研究为支持美国环境保护署(U.S. EPA)和其他利益相关者将健康结果研究纳入政策制定提供了证据。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Causal Inference Methods for Estimating Long-Term Health Effects of Air Quality Regulations.

Introduction: The regulatory and policy environment surrounding air quality management warrants new types of epidemiological evidence. Whereas air pollution epidemiology has typically informed previous policies with estimates of exposure-response relationships between pollution and health outcomes, new types of evidence can inform current debates about the actual health impacts of air quality regulations. Directly evaluating specific regulatory strategies is distinct from and complements estimating exposure-response relationships; increased emphasis on assessing the effectiveness of well-defined regulatory interventions will enhance the evidence supporting policy decisions. The goal of this report is to provide new analytic perspectives and statistical methods for what we refer to as "direct"-accountability assessment of the effectiveness of specific air quality regulatory interventions. Toward this end, we sharpened many of the distinctions surrounding accountability assessment initially raised by the HEI Accountability Working Group (2003) through discussion, development, and deployment of statistical methods for drawing causal inferences from observational data. The methods and analyses presented here are unified in their focus on anchoring accountability assessment to the estimation of the causal consequences of well-defined actions or interventions. These analytic perspectives are discussed in the context of two direct-accountability case studies pertaining to four different links in the so-called chain of accountability, the related series of events leading from the intervention to the expected outcomes (see Preface; HEI Accountability Working Group 2003).

Methods: The statistical methods described in this report consist of both established methods for drawing causal inferences from observational data and newly developed methods for assessing causal accountability. We have sharpened the analytic distinctions between studies that directly evaluated the effectiveness of specific policies and those that estimated exposure-response relationships between pollution and health. We emphasized how a potential-outcomes paradigm for causal inference can elevate policy debates by means of more direct evidence of the extent to which complex regulatory interventions affect pollution and health outcomes. We also outlined the potential-outcomes perspective and promoted its use as a means to frame observational studies as approximate randomized experiments. Our newly developed methods for assessing causal accountability draw on propensity scores, principal stratification, causal mediation analysis, spatial hierarchical models, and Bayesian estimation. The first case study made use of health outcomes among approximately four million Medicare beneficiaries living in the Western United States to estimate the causal health impacts of areas designated as being in nonattainment for particulate matter ≤10 μm in aerodynamic diameter (PM10*) according to the 1987 National Ambient Air Quality Standards (NAAQS). The second case study focused on developing and testing our new, advanced methodology for multipollutant accountability assessment by examining the extent to which sulfur dioxide (SO2) scrubbers on coal-fired power plants causally affect emissions of SO2, nitrogen oxides (NO(x)), and carbon dioxide (CO2) as well as the extent to which emissions reductions mediate the causal effect of a scrubber on ambient concentrations of PM2.5. Both case studies were anchored in our compilation of national, linked data on ambient air quality monitoring, weather, population demographics, Medicare hospitalization and mortality outcomes, continuous-emissions monitoring for electricity-generating units (EGUs) in power plants, and a variety of regulatory control interventions. The resulting database has unprecedented accuracy and granularity for conducting the types of accountability assessments presented in this report. A key component of our work was the creation of tools to help distribute our linked database and to facilitate reproducible research.

Results: In the first case study, we focused on illustrating the most fundamental features of a causal-inference perspective on direct-accountability assessment. The results indicated that all-cause Medicare mortality and respiratory-related hospitalization rates were causally reduced in areas designated as nonattainment for PM10 during 1990 to 1995 compared with the rates that would have occurred without the designation. In the second case study, which examined power-plant emissions and illustrated our newly developed statistical methods, the results indicated that the presence of an SO2 scrubber causally reduced ambient PM2.5 and that this reduction was mediated almost entirely through causal reductions in SO2 emissions. The results were interpreted in light of the well-documented relationships between scrubbers, power-plant emissions, and PM2.5.

Conclusion: By grounding accountability research in a potential-outcomes framework and applying our new methods to our collection of national data sets, we were able to provide additional sound evidence of the health effects of long-term, large-scale air quality regulations. This additional, rigorous evidence of the causal effects of well-defined actions augments the existing body of research and ensures that the highest-level epidemiological evidence will continue to support regulatory policies. Ultimately, our research contributed to the evidence available to support to the U.S. Environmental Protection Agency (U.S. EPA) and other stakeholders for incorporating health outcomes research into policy development.

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