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室内暴露于细气溶胶和酸性气体。

Indoor exposures to fine aerosols and acid gases.

作者信息

Koutrakis P, Brauer M, Briggs S L, Leaderer B P

机构信息

Harvard School of Public Health, Boston, MA 02115.

出版信息

Environ Health Perspect. 1991 Nov;95:23-8. doi: 10.1289/ehp.919523.

Abstract

Indoor exposures to aerosols and gases are associated with both indoor and outdoor air pollution sources. The identification of sources and the assessment of their relative contribution can be a complicated process due to a) the presence of numerous indoor sources, which can vary from building to building; b) the uncertainties associated with the estimation of the impact of outdoor sources on indoor air quality; c) the interactions between pollutants; and d) the importance of reactions between pollutants and indoor surfaces. It is well established that fine particles (diameter less than or equal to 2.5 microns) originating from outdoor sources such as automobiles, oil and coal combustion, incineration, and diverse industrial activities can penetrate into the indoor environment. Indoor/outdoor ratios, usually varying between 0.4 and 0.8, depend on parameters such as particle size and density, air exchange rate, and the surface-to-volume ratio of the indoor environment. Determining fine particle elemental composition makes it possible to identify the contribution of different outdoor sources. This paper focuses on the origin and the concentration of indoor aerosols and acid gases by highlighting the results from two indoor air quality studies.

摘要

室内接触气溶胶和气体与室内和室外空气污染来源都有关联。由于以下原因,确定污染源及其相对贡献可能是一个复杂的过程:a) 存在众多室内污染源,不同建筑物的污染源可能不同;b) 估算室外污染源对室内空气质量影响时存在不确定性;c) 污染物之间的相互作用;d) 污染物与室内表面反应的重要性。众所周知,源自汽车、石油和煤炭燃烧、焚烧及各种工业活动等室外污染源的细颗粒物(直径小于或等于2.5微米)能够渗入室内环境。室内/室外比率通常在0.4至0.8之间变化,这取决于颗粒大小和密度、空气交换率以及室内环境的表面积与体积比等参数。确定细颗粒物的元素组成有助于识别不同室外污染源的贡献。本文通过突出两项室内空气质量研究的结果,重点探讨室内气溶胶和酸性气体的来源及浓度。

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