Halios Christos H, Helmis Costas G
Department of Applied Physics, Faculty of Physics, University of Athens, Building Phys 5, University Campus, Athens 15784, Greece.
Sci Total Environ. 2007 Aug 1;381(1-3):222-32. doi: 10.1016/j.scitotenv.2007.03.012. Epub 2007 Apr 26.
Indoor exposure to air contaminants penetrating from the outdoor environment depends on a number of key processes and parameters such as the ventilation rate, the geometric characteristics of the indoor environment, the outdoor concentration and the indoor removal mechanisms. In this study two alternative methods are used, an analytical and a numerical one, in order to study the time lag and the reduction of the variances of the indoor concentrations, and to estimate the deposition rate of the air contaminants in the indoor environment employing both indoor and outdoor measurements of air contaminants. The analytical method is based on a solution of the mass balance equation involving an outdoor concentration pulse which varies sinusoidally with the time, while the numerical method involves the application of the MIAQ indoor air quality model assuming a triangular pulse. The ratio of the fluctuation of the indoor concentrations to the outdoor ones and the time lag were estimated for different values of the deposition velocity, the ventilation rate and the duration of the outdoor pulse. Results have showed that the time lag between the indoor and outdoor concentrations is inversely proportional to the deposition and ventilation rates, while is proportional to the duration of the outdoor pulse. The decrease of the ventilation and the deposition rate results in a rapid decrement of the variance ratio of indoor to outdoor concentrations and to an increment of the variance ratio, respectively. The methods presented here can be applied for gaseous species as well as for particulate matter. The nomograms and theoretical relationships that resulted from the simulation results and the analytical methods respectively were used in order to study indoor air phenomena. In particular they were used for the estimation of SO2 deposition rate. Implications of the studied parameters to exposure studies were estimated by calculating the ratio of the indoor exposure to the exposure outdoors. Limitations of the methods were explored by testing various scenarios which are usually met in the indoor environment. Strong indoor emissions, intense chemistry and varying ventilation rates (opening and closing of the windows) were found to radically influence the time lag and fluctuation ratios.
室内暴露于从室外环境渗透进来的空气污染物,取决于许多关键过程和参数,如通风率、室内环境的几何特征、室外浓度以及室内去除机制。在本研究中,使用了两种替代方法,一种是解析法,另一种是数值法,以研究时间滞后和室内浓度方差的降低情况,并利用室内和室外空气污染物测量数据来估算室内环境中空气污染物的沉积速率。解析法基于一个质量平衡方程的解,该方程涉及一个随时间呈正弦变化的室外浓度脉冲,而数值法则涉及应用假设为三角脉冲的MIAQ室内空气质量模型。针对沉积速度、通风率和室外脉冲持续时间的不同值,估算了室内浓度与室外浓度的波动比以及时间滞后。结果表明,室内和室外浓度之间的时间滞后与沉积速率和通风率成反比,而与室外脉冲的持续时间成正比。通风率和沉积速率的降低分别导致室内与室外浓度方差比的快速下降和方差比的增加。这里介绍的方法可应用于气态物质以及颗粒物。分别由模拟结果和解析方法得出的列线图和理论关系,被用于研究室内空气现象。特别是它们被用于估算二氧化硫的沉积速率。通过计算室内暴露与室外暴露的比值,估算了所研究参数对暴露研究的影响。通过测试室内环境中通常会遇到的各种场景,探讨了这些方法的局限性。发现强烈的室内排放、剧烈的化学反应和变化的通风率(窗户的打开和关闭)会从根本上影响时间滞后和波动比。