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Micro-aerobic granulation for actual coking wastewater treatment in an expanded granular sludge bed (EGSB) reactor: Intermittent oxygenation

机译:用于膨胀粒状污泥床(EGSB)反应器中的实际焦化废水处理的微食造粒机:间歇氧合

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To accomplish rapidly the micro-aerobic granulation process of digestion sludge for the treatment of actual coking wastewater and meanwhile achieve high COD, the EGSB reactor was employed with two operation stages. Stage I: Granular sludge was formed from digestion sludge using brewery wastewater as substrate in the anaerobic way (meanwhile adding little granules, which were 1/7 of the total biomass). Stage II: Granular sludge was acclimatized with the actual coking wastewater through intermittent micro-oxygenation way of 800–20000ml·min−1 18–12 times at 20–60min intervals, 1h each time. The experimental results showed that the granular sludge could quickly form in 10d in the EGSB reactor seeded with digestion sludge and little loose granules. It took only about 6 months for the successful micro-aerobic acclimating of the granular sludge by the actual coking wastewater. With 631–1220mg·L−1 influent COD concentration, 1.0L·h−1 influent flow, 12h HRT, 20000ml.min−1 air flow and 3g·L−1 NaHCO3 supplement, the micro-aerobic EGSB reactor could have 75% high COD removal efficiency. The actual coking wastewater was not restrain the granules at the primary stage (at least for more than 1 month), but at 4 months, the SMA reduced 62.9% compared with the parallel, before treating CWW. The supplement of some oxygen and NaHCO3 was very important. Directly using the actual coking wastewater and through an intermittent oxygenation way was an effective acclimation approach.
机译:为了迅速实现消化污泥的微食造粒方法,用于治疗实际焦化废水,同时实现高鳕鱼,使用两个操作阶段。 I阶段I:颗粒污泥由使用啤酒废水作为厌氧方式的底物的消化污泥形成(同时添加小颗粒,为总生物质的1/7)。 II阶段:通过间歇微氧化方式通过800-20000ml· min − 1 18-12次以20-60min的间隔,每隔6小时时间。实验结果表明,用消化污泥和少量松散颗粒,粒状污泥在替换污泥和少量松散的颗粒中可以在10D中迅速形成。实际焦化废水的成功微食灌装成功的微量化适应性花了大约6个月。用631-1220mg· l − 1 流动的cod浓度,1.0l· h − 1 流水流,12h hrt,20000ml。 min − 1 空气流量和3g· l − 1 nahco 3 补充剂,Micro-abobic Egsb反应器可以具有75%的COD去除效率。实际的焦化废水不是在初级阶段(至少超过1个月)的颗粒(至少超过1个月),但在4个月时,SMA与平行相比减少了62.9%,然后在治疗CWW之前比较。一些氧气和Nahco 3 的补充非常重要。直接使用实际的焦化废水和间歇氧化方式是一种有效的适应方法。

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