首页> 外文会议>Biennial conference of the International Association on Water Quality >ALPHA CORRECTION FACTORS FOR STATIC AERATORS AND FINE BUBBLE DIFFUSERS USED IN MUNICIPAL FACULTATIVE AERATED LAGOONS
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ALPHA CORRECTION FACTORS FOR STATIC AERATORS AND FINE BUBBLE DIFFUSERS USED IN MUNICIPAL FACULTATIVE AERATED LAGOONS

机译:市政人工充气泻湖中使用的静态曝气器和细气泡扩散器的阿尔法校正因子

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The alpha correction factor (K_L a process water/K_La clean water; where K_La is the volumetric oxygen mass transfer coefficient) was evaluated for 4 kinds of static aerators and 2 kinds of fine bubble diffusers used in municipal facultative aerated lagoons. For this purpose, a 40 m~3 steel tank was filled (3.1 m side water depth) with clean or process water. The process water consisted of "mixed liquor" from a municipal facultative aerated lagoon divided into a cascade of four identical basins that were 3.5 m deep. Results showed that in the last three basins, the alpha correction factors were relatively high, being between 0.85 to 0.95 for any type of aeration device. In the first lagoon, however, the alpha correction factors were between 0.70 and 0.90 for static aerators and about 0.70 for fine bubble diffusers. Furthermore, at the inlet of the first basin, the alpha factor was as low as 0.59 for a static aerator and 0.26 for a fine bubble diffuser, due to the composition of the "mixed liquor". It was shown that the alpha correction factor that should be used for the design of aeration systems for facultative aerated lagoons should be lower in the first basin of a series of basins and could be higher than 0.85 for the downstream basins.
机译:针对市政兼用充气泻湖中使用的4种静态曝气器和2种细微气泡扩散器,评估了α校正因子(K_L为工艺用水/ K_La净水;其中K_La为体积氧气传质系数)。为此,在40 m〜3的钢制水箱中(侧面水深3.1 m)填充了清洁水或工艺用水。加工用水由市政混合曝气泻湖中的“混合液”组成,分为四个相同的深3.5 m的盆地。结果表明,在后三个盆地中,α校正因子相对较高,任何类型的曝气设备的α校正因子都在0.85至0.95之间。但是,在第一个泻湖中,静态曝气器的alpha校正因子在0.70到0.90之间,细小气泡扩散器的alpha校正因子在0.70左右。此外,由于“混合液”的组成,在第一盆的入口处,对于静态曝气器,α因子低至0.59,对于细微气泡扩散器,α因子低至0.26。结果表明,在一系列盆地的第一个盆地中,用于兼性充气泻湖曝气系统设计的alpha校正因子应较低,而在下游盆地中,α校正因子应高于0.85。

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