School of Population and Public Health, The University of British Columbia, Vancouver, Canada; Department of Environmental Health Sciences, School of Public Health and Health Sciences, University of Massachusetts, Amherst, MA, USA.
School of Population and Public Health, The University of British Columbia, Vancouver, Canada.
Environ Int. 2018 May;114:307-317. doi: 10.1016/j.envint.2018.02.033. Epub 2018 Mar 19.
Household air pollution (HAP) from combustion of solid fuels is an important contributor to disease burden in low- and middle-income countries (LIC, and MIC). However, current HAP disease burden estimates are based on integrated exposure response curves that are not currently informed by quantitative HAP studies in LIC and MIC. While there is adequate evidence supporting causal relationships between HAP and respiratory disease, large cohort studies specifically examining relationships between quantitative measures of HAP exposure with cardiovascular disease are lacking.
We aim to improve upon exposure proxies based on fuel type, and to reduce exposure misclassification by quantitatively measuring exposure across varying cooking fuel types and conditions in diverse geographies and socioeconomic settings. We leverage technology advancements to estimate household and personal PM (particles below 2.5 μm in aerodynamic diameter) exposure within the large (N250,000) multi-country (N26) Prospective Urban and Rural Epidemiological (PURE) cohort study. Here, we detail the study protocol and the innovative methodologies being used to characterize HAP exposures, and their application in epidemiologic analyses.
METHODS/DESIGN: This study characterizes HAP PM exposures for participants in rural communities in ten PURE countries with >10% solid fuel use at baseline (Bangladesh, Brazil, Chile, China, Colombia, India, Pakistan, South Africa, Tanzania, and Zimbabwe). PM monitoring includes 48-h cooking area measurements in 4500 households and simultaneous personal monitoring of male and female pairs from 20% of the selected households. Repeat measurements occur in 20% of households to assess impacts of seasonality. Monitoring began in 2017, and will continue through 2019. The Ultrasonic Personal Aerosol Sampler (UPAS), a novel, robust, and inexpensive filter based monitor that is programmable through a dedicated mobile phone application is used for sampling. Pilot study field evaluation of cooking area measurements indicated high correlation between the UPAS and reference Harvard Impactors (r = 0.91; 95% CI: 0.84, 0.95; slope = 0.95). To facilitate tracking and to minimize contamination and analytical error, the samplers utilize barcoded filters and filter cartridges that are weighed pre- and post-sampling using a fully automated weighing system. Pump flow and pressure measurements, temperature and RH, GPS coordinates and semi-quantitative continuous particle mass concentrations based on filter differential pressure are uploaded to a central server automatically whenever the mobile phone is connected to the internet, with sampled data automatically screened for quality control parameters. A short survey is administered during the 48-h monitoring period. Post-weighed filters are further analyzed to estimate black carbon concentrations through a semi-automated, rapid, cost-effective image analysis approach. The measured PM data will then be combined with PURE survey information on household characteristics and behaviours collected at baseline and during follow-up to develop quantitative HAP models for PM exposures for all rural PURE participants (~50,000) and across different cooking fuel types within the 10 index countries. Both the measured (in the subset) and the modelled exposures will be used in separate longitudinal epidemiologic analyses to assess associations with cardiopulmonary mortality, and disease incidence.
The collected data and resulting characterization of cooking area and personal PM exposures in multiple rural communities from 10 countries will better inform exposure assessment as well as future epidemiologic analyses assessing the relationships between quantitative estimates of chronic HAP exposure with adult mortality and incident cardiovascular and respiratory disease. This will provide refined and more accurate exposure estimates in global CVD related exposure-response analyses.
来自固体燃料燃烧的家庭空气污染(HAP)是低收入和中等收入国家(LIC 和 MIC)疾病负担的重要因素。然而,目前的 HAP 疾病负担估计是基于综合暴露反应曲线,这些曲线目前没有得到 LIC 和 MIC 中定量 HAP 研究的支持。虽然有足够的证据支持 HAP 与呼吸道疾病之间存在因果关系,但缺乏专门研究定量 HAP 暴露与心血管疾病之间关系的大型队列研究。
我们旨在改进基于燃料类型的暴露指标,并通过在不同地理位置和社会经济环境中对不同烹饪燃料类型和条件下的暴露进行定量测量,减少暴露分类错误。我们利用技术进步来估计大型(N250,000)多国家(N26)前瞻性城市和农村流行病学(PURE)队列研究中家庭和个人 PM(空气动力学直径小于 2.5μm 的颗粒)暴露。在这里,我们详细介绍了研究方案和用于描述 HAP 暴露的创新方法,以及它们在流行病学分析中的应用。
方法/设计:本研究对 10 个 PURE 国家中基线时使用超过 10%固体燃料的农村社区的参与者进行 HAP PM 暴露特征描述(孟加拉国、巴西、智利、中国、哥伦比亚、印度、巴基斯坦、南非、坦桑尼亚和津巴布韦)。PM 监测包括在 4500 个家庭中进行 48 小时的烹饪区域测量,以及从 20%选定家庭中同时对男性和女性对进行个人监测。在 20%的家庭中进行重复测量,以评估季节性的影响。监测于 2017 年开始,并将持续到 2019 年。使用新型、坚固且廉价的基于过滤器的 Ultrasonic Personal Aerosol Sampler(UPAS)进行采样,该监测器可通过专用移动电话应用程序进行编程。对烹饪区域测量的初步研究现场评估表明,UPAS 和参考 Harvard Impactors 之间高度相关(r=0.91;95%置信区间:0.84,0.95;斜率=0.95)。为了便于跟踪,并最大程度地减少污染和分析误差,采样器使用带有条形码的过滤器和过滤器盒,在采样前后使用全自动称重系统进行称重。每当移动电话连接到互联网时,泵流量和压力测量值、温度和 RH、GPS 坐标和基于过滤器差分压力的半定量连续颗粒质量浓度会自动上传到中央服务器,并自动对采样数据进行质量控制参数筛选。在 48 小时监测期间进行简短调查。对经过称重的过滤器进行进一步分析,通过半自动、快速、具有成本效益的图像分析方法来估计黑碳浓度。然后,将测量的 PM 数据与 PURE 调查信息(包括家庭特征和行为)结合起来,为所有农村 PURE 参与者(约 50,000 人)和 10 个索引国家内的不同烹饪燃料类型开发 PM 暴露的定量 HAP 模型。在单独的纵向流行病学分析中,将使用测量的(在子集中)和建模的暴露情况来评估与心肺死亡率以及疾病发病率之间的关联。
从 10 个国家的多个农村社区收集的数据和对烹饪区和个人 PM 暴露的描述,将更好地进行暴露评估,以及未来评估慢性 HAP 暴露与成人死亡率以及心血管和呼吸道疾病发病率之间定量关系的流行病学分析。这将为全球 CVD 相关暴露反应分析提供更精确和更准确的暴露估计。