| Literature DB >> 36141667 |
Jianwu Chen1,2, Longzhe Jin1, Bin Yang1,2, Zhenfang Chen2, Guoliang Zhang1.
Abstract
Local exhaust ventilation is an important method of contamination control, and the type of exhaust hood and the air distribution at the hood face have an important influence on the contamination control effect. When the hood face is large, it is difficult to create a uniform airflow distribution at the hood face, which if achieved, could improve the effect of contamination control. To that end, the large-area workbench used in the process of vaccine purification was taken as the research subject prototype for this study. According to the methods for generating a uniform airflow distribution at the hood face, the lower exhaust workbenches of four structures were established using CAD and simulated using Ansys Fluent. The best uniformity of workbench surface air distribution was with Structure-4, while the worst was with Structure-1. The workbench surface airflow distribution could not achieve uniformity when only an inclined bottom was used for the large-area lower exhaust workbench with one side outlet. The more internal slits there were, the greater the air distribution area and the more uniform the air distribution. The width of the area of workbench surface airflow distribution was determined by the width of the slits. The numerical simulation results were verified by experiments, which showed them to be credible.Entities:
Keywords: airflow distribution; contamination control; lower exhaust hood; uniform airflow; workbench
Mesh:
Year: 2022 PMID: 36141667 PMCID: PMC9517492 DOI: 10.3390/ijerph191811395
Source DB: PubMed Journal: Int J Environ Res Public Health ISSN: 1660-4601 Impact factor: 4.614
Figure 1The large-area workbench prototype used in this study.
Figure 2The methods for achieving a uniform airflow distribution at the hood face. θ is the inclination.
Figure 3Four geometries of the lower exhaust workbench studied in this paper.
Figure 4Lower exhaust workbench used for experimental validation.
Solver parameter settings.
| Solver Parameters | Parameter Settings |
|---|---|
| Solver type | Pressure-based |
| Solver velocity formulation | Absolute |
| Solver time | Steady |
| Viscous model | Standard |
| Species transport | Off |
| Energy | Off |
| Pressure–velocity coupling | SIMPLEC |
| Spatial discretization | Second order upwind |
| Convergence criterion | 10−6 |
| Interaction to plot and store | 1000 |
| Wall condition | Stationary wall/No slip |
Settings of boundary conditions.
| Boundary Conditions | Parameter Settings |
|---|---|
| Outlet | Surface of lower exhaust workbench |
| Outlet boundary type | Pressure outlet |
| Gauge pressure (Pa) | 0 |
| Inlet | Air outlet of elbow |
| Inlet boundary type | Velocity inlet |
| Velocity at inlet (m/s) | –5 |
| Material | Air |
| Air viscosity (kg/m/s) | 1.81 × 10−5 |
| Hydraulic diameter of inlet (m) | 0.48 |
| Turbulence intensity of inlet (%) | 3.81 |
Figure 5Variation of air velocity under different grid division schemes for Structure-1.
Figure 6Experimental validation of lower exhaust workbench and measurement conditions.
Figure 7Layout of velocity measure points at the surface of the workbench.
Figure 8Velocity contour maps for differently structured workbenches. (a) Velocity contour map of a vertical section at the center of the workbench; (b) velocity contour map of the workbench surface.
Figure 9Workbench surface center velocity in the short side direction for differently structured workbenches studied in this paper.
Figure 10Velocity vector maps for four differently structured workbenches.
Figure 11Measured velocities along five lines and simulated velocities along the centerline.