Zhang Zi-Jian, Wu Wei-Wei, Wang Jian-Long
Laboratory of Environmental Technology, INET, Tsinghua University, Beijing 100084, China.
Huan Jing Ke Xue. 2010 Jan;31(1):140-6.
The formation of aerobic granular sludge was investigated by seeding completely autotrophic nitrifying sludge in sequencing batch reactors (SBR) using synthetic wastewater containing ammonia in the range of 120-650 mg/L under the loading rates of 0.48-3.60 kg/(m3 x d). The experimental results indicated that the granular sludge could be formed on day 22 in SBR by inoculating nitrifying sludge when ammonium loading rate was 0.48 kg/(m3 x d), temperature was 30 degrees C +/- 2 degrees C and the settling time was gradually decreased to 10 min. The size variation of granular sludge underwent three stages: stagnant, rapid increase and stable stages. The granules kept increasing in size to around 500 microm at rate of 12 microm/d and became stable on 43 days. The mature granules held regular shapes and clear outline. The granular sludge with diameter larger than 300 microm accounted for 74.6%, there was almost no flocculate sludge in the reactor. During the granulation process, the color of the sludge became yellow reddish from grey. There were great amount of bacillus and clump of EPS distributed on the surface of granular sludge.
通过在序批式反应器(SBR)中接种完全自养硝化污泥,使用氨含量在120 - 650 mg/L范围内的合成废水,在0.48 - 3.60 kg/(m³·d)的负荷率下,研究了好氧颗粒污泥的形成。实验结果表明,当氨负荷率为0.48 kg/(m³·d)、温度为30℃±2℃且沉降时间逐渐降至10分钟时,在SBR中接种硝化污泥后第22天可形成颗粒污泥。颗粒污泥的尺寸变化经历三个阶段:停滞、快速增长和稳定阶段。颗粒以12 μm/d的速率持续增大至约500 μm,并在第43天变得稳定。成熟颗粒形状规则、轮廓清晰。直径大于300 μm的颗粒污泥占74.6%,反应器中几乎没有絮凝污泥。在颗粒化过程中,污泥颜色从灰色变为黄红色。颗粒污泥表面分布有大量杆菌和EPS团块。