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首页> 外文期刊>Journal of Fluid Mechanics >Passive scalar dispersion in a turbulent boundary layer from a line source at the wall and downstream of an obstacle
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Passive scalar dispersion in a turbulent boundary layer from a line source at the wall and downstream of an obstacle

机译:来自障碍物壁和下游的线源的湍流边界层中的被动标量色散

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Simultaneous measurements of the velocity and scalar concentration fields have been made in the plume emitting from a two-dimensional line source at the wall. The source is one obstacle height, h, downstream of a two-dimensional square obstacle located on the wall of a turbulent boundary layer. These measurements were made in two fluid media: water and air. In both media particle image velocimetry (PIV) was used for the velocity field measurements. For the scalar concentration measurements laser-induced fluorescence (LIF) was used for the water flow and Mie scattering diffusion (MSD) for the air how Profiles of the mean and root-mean-square streamwise and wall-normal velocity components, Reynolds shear stress and mean and root-mean-square scalar concentration were determined at x = 4h and 6h downstream of the obstacle in the recirculation region and above it in the mixing region. At these streamwise stations the scalar fluxes, (uc) over bar and (vc) over bar, were also determined from the simultaneous velocity and scalar concentration field data. Both of these fluxes change sign from negative to positive with increasing distance from the wall in the recirculating region at 4h. A conditional analysis of the data was carried out by sorting them into the eight categories (octants) given by the sign combinations of the three variables: +/-u, +/-v and +/-c. The octants with combinations of these three variables that correspond to types of scalar concentration flux motions that can be approximated by mean gradient scalar transport models are the octants that make the dominant contributions to (uc) over bar and (vc) over bar. However, in the recirculating zone, counter-gradient transport type motions also make significant contributions. Based on this conditional analysis, second-order mean gradient models of the scalar and the momentum fluxes were constructed; they compare well to the measured values at 4h and 6h, particularly for the streamwise scalar flux, (uc) over bar. Additional measurements of the velocity and concentration fields were made further downstream of the reattachment location in the wake region of the air flow. The mean velocity deficit profile determined from these measurements at x = 20h compares quite well to a similarity solution profile obtained by Counihan, Hunt & Jackson (1974). Their analysis was extended in the present investigation to the concentration field. The similarity solution obtained for the mean concentration compares well to profiles measured at x = 12h, 15h, and 20h, up to about three obstacle heights above the wall. [References: 30]
机译:在壁上的二维线源发出的羽流中,已经同时测量了速度和标量浓度场。源是位于湍流边界层壁上的二维方形障碍物下游的一个障碍物高度h。这些测量是在两种流体介质中进行的:水和空气。在两种介质中,均使用粒子图像测速仪(PIV)进行速度场测量。在标量浓度测量中,激光诱导荧光(LIF)用于水流,空气使用Mie散射扩散(MSD),平均和均方根流向和壁法向速度分量的分布图,雷诺剪切应力在再循环区障碍物下游和混合区障碍物上游x = 4h和6h处确定均值和均方根标量浓度。在这些沿流站,还根据同时的速度和标量浓度场数据确定了标量通量,即在棒上的(uc)和在棒上的(vc)。随着在4h时与再循环区域中与壁的距离增加,这两个通量都从负变为正。对数据进行条件分析,方法是将数据分为+/- u,+ /-v和+/- c三个变量的符号组合,分为八类(八分位数)。具有这三个变量的组合的八分位数对应于标量浓度通量运动类型,可以通过平均梯度标量传输模型来近似,这些八分位数是对(uc)超过bar和(vc)超过bar的主要贡献。但是,在再循环区中,反梯度运输类型的运动也做出了重要贡献。在此条件分析的基础上,建立了标量和动量通量的二阶平均梯度模型。它们与4h和6h时的测量值比较好,特别是在棒上的流式标量通量(uc)上。在气流尾流区域中重新连接位置的更下游,对速度场和浓度场进行了其他测量。由这些测量在x = 20h处确定的平均速度赤字曲线与Counihan,Hunt&Jackson(1974)获得的相似性解决方案曲线相当好。他们的分析在目前的研究中扩展到了浓度领域。对于平均浓度获得的相似性解决方案与在x = 12h,15h和20h处(在壁上方大约三个障碍物高度处)测得的轮廓很好地比较。 [参考:30]

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