Division of Pulmonary and Critical Care, School of Medicine, Johns Hopkins University, Baltimore, USA.
Division of Pulmonary and Critical Care, School of Medicine, Johns Hopkins University, Baltimore, USA; Nepal Nutrition Intervention Project Sarlahi, Kathmandu, Nepal.
Environ Res. 2015 Oct;142:424-31. doi: 10.1016/j.envres.2015.07.012. Epub 2015 Jul 31.
Household air pollution from the burning of biomass fuels is recognized as the third greatest contributor to the global burden of disease. Incomplete combustion of biomass fuels releases a complex mixture of carbon monoxide (CO), particulate matter (PM) and other toxins into the household environment. Some investigators have used indoor CO concentrations as a reliable surrogate of indoor PM concentrations; however, the assumption that indoor CO concentration is a reasonable proxy of indoor PM concentration has been a subject of controversy. We sought to describe the relationship between indoor PM2.5 and CO concentrations in 128 households across three resource-poor settings in Peru, Nepal, and Kenya. We simultaneously collected minute-to-minute PM2.5 and CO concentrations within a meter of the open-fire stove for approximately 24h using the EasyLog-USB-CO data logger (Lascar Electronics, Erie, PA) and the personal DataRAM-1000AN (Thermo Fisher Scientific Inc., Waltham, MA), respectively. We also collected information regarding household construction characteristics, and cooking practices of the primary cook. Average 24h indoor PM2.5 and CO concentrations ranged between 615 and 1440 μg/m(3), and between 9.1 and 35.1 ppm, respectively. Minute-to-minute indoor PM2.5 concentrations were in a safe range (<25 μg/m(3)) between 17% and 65% of the time, and exceeded 1000 μg/m(3) between 8% and 21% of the time, whereas indoor CO concentrations were in a safe range (<7 ppm) between 46% and 79% of the time and exceeded 50 ppm between 4%, and 20% of the time. Overall correlations between indoor PM2.5 and CO concentrations were low to moderate (Spearman ρ between 0.59 and 0.83). There was also poor agreement and evidence of proportional bias between observed indoor PM2.5 concentrations vs. those estimated based on indoor CO concentrations, with greater discordance at lower concentrations. Our analysis does not support the notion that indoor CO concentration is a surrogate marker for indoor PM2.5 concentration across all settings. Both are important markers of household air pollution with different health and environmental implications and should therefore be independently measured.
来自生物质燃料燃烧的家庭空气污染被认为是导致全球疾病负担的第三大因素。生物质燃料不完全燃烧会向家庭环境中释放出一氧化碳(CO)、颗粒物(PM)和其他毒素的复杂混合物。一些研究人员使用室内 CO 浓度作为室内 PM 浓度的可靠替代物;然而,室内 CO 浓度是室内 PM 浓度的合理替代物的假设一直存在争议。我们试图描述在秘鲁、尼泊尔和肯尼亚的三个资源匮乏地区的 128 户家庭中,室内 PM2.5 和 CO 浓度之间的关系。我们使用 EasyLog-USB-CO 数据记录仪(Lascar Electronics,Erie,PA)和个人 DataRAM-1000AN(Thermo Fisher Scientific Inc.,Waltham,MA)在距离开放式炉灶 1 米范围内,分别在 24 小时内每分钟收集 PM2.5 和 CO 浓度。我们还收集了有关家庭建筑特征和主要厨师烹饪习惯的信息。平均 24 小时室内 PM2.5 和 CO 浓度范围分别为 615 至 1440μg/m(3)和 9.1 至 35.1ppm。室内 PM2.5 浓度在 17%至 65%的时间处于安全范围(<25μg/m(3)),8%至 21%的时间超过 1000μg/m(3),而室内 CO 浓度在 46%至 79%的时间处于安全范围(<7ppm),4%至 20%的时间超过 50ppm。室内 PM2.5 和 CO 浓度之间的总体相关性较低至中等(Spearman ρ 值在 0.59 至 0.83 之间)。观察到的室内 PM2.5 浓度与基于室内 CO 浓度估计的浓度之间的一致性也很差,存在比例偏差的证据,在浓度较低时差异更大。我们的分析不支持室内 CO 浓度是所有环境中室内 PM2.5 浓度替代物的观点。两者都是家庭空气污染的重要标志物,具有不同的健康和环境影响,因此应独立测量。