排放模型与计算流体动力学模拟的比较及改进模型。

J. Bennett, C. Feigley, J. Khan, M. Hosni
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引用次数: 10

摘要

了解污染源的行为对于控制空气污染物的暴露非常重要。工业卫生学家经常被要求从室内浓度数据中推断出排放信息。这是不容易做到的,但经常使用对污染物运输作出简化假设的模型。这些假设造成的错误还没有得到很好的理解。本研究比较了单区完全混合(CM-1)、两区完全混合(CM-2)和均匀扩散(UD)模型的排放估计,并将排放设置为计算流体动力学(CFD)模拟工作场所的边界条件。利用Fluent 4计算室内气流场和浓度场。这些数值实验是三个源位置、五个受体位置、三个稀释气流速率和两个生成速率曲线(恒定和时变)的因子组合。其目的是计算合理的浓度场,而不是模拟真实工作室中的过程。因此,误差在这里被定义为模型和CFD预测之间的差异。对于稳态情况,UD模型的误差最小。当源近场含有呼吸带受体时,采用CM-2模型。其次是UD、CM-2和CM-1。对所有源和受体位置进行平均(CM-2仅适用于一个位置),与CFD的一致性从低到低依次为UD、CM-1和CM-2。源和受体位置对CM-1模型估计的排放有较大影响,对UD模型估计的排放有一定影响。利用稳态浓度梯度衍生的位置特定混合因子(位置因子),建立了更精确的随时间变化的排放模型CM-L。CM-L最准确地模拟了时变源发射的总质量,其次是CM-1和CM-2。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Comparison of emission models with computational fluid dynamic simulation and a proposed improved model.
Understanding source behavior is important in controlling exposure to airborne contaminants. Industrial hygienists are often asked to infer emission information from room concentration data. This is not easily done, but models that make simplifying assumptions regarding contaminant transport are frequently used. The errors resulting from these assumptions are not yet well understood. This study compares emission estimates from the single-zone completely mixed (CM-1), two-zone completely mixed (CM-2), and uniform diffusivity (UD) models with the emissions set as boundary conditions in computational fluid dynamic (CFD) simulations of a workplace. The room airflow and concentration fields were computed using Fluent 4. These numerical experiments were factorial combinations of three source locations, five receptor locations, three dilution airflow rates, and two generation rate profiles, constant and time-varying. The aim was to compute plausible concentration fields, not to simulate exactly the processes in a real workroom. Thus, error is defined here as the difference between model and CFD predictions. For the steady-state case the UD model had the lowest error. When the source near-field contained the breathing zone receptor, the CM-2 model was applied. Then, in decreasing agreement with CFD were UD, CM-2, and CM-1. Averaging over all source and receptor locations (CM-2 applied for only one), in decreasing order of agreement with CFD were UD, CM-1, and CM-2. Source and receptor location had large effects on emission estimates using the CM-1 model and some effect using the UD model. A location-specific mixing factor (location factor) derived from steady-state concentration gradients was used to build a more accurate time-dependent emission model, CM-L. Total mass emitted from a time-varying source was modeled most accurately by CM-L, followed by CM-1 and CM-2.
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