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Enhancement Biosorption of Activated Sludge Process on Heavy Metals: Cadmium (Cd) And Nickel (Ni)

机译:增强活性污泥加工的生物吸附重金属:镉(CD)和镍(Ni)

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摘要

This study focuses on Actived sludge treatment is carried out by a continuous reactor. Merriote tube capacity of 10L with a discharge of 10L/day as an inlet. Next to the 10L volume aeration tank where biological treatment occurs, pH 7 ± 0.2 and DO ≥ 3mg/L are the control variables. COD, Cd and Ni are taken for testing inlet and outlet. Artificial waste is used as an inlet with a nutrient ratio of C: N: P is 100: 5: 1. Seeding stage occurs 13 days to get an MLSS value ≥ 2000mg / L. Acclimatization I for adapting microorganisms to the environment occurred for 27 days and acclimatization II for 11 days as microbial ada ptation to heavy metals. Increasing t h e C / N ratio f ro m 20 to 50 will reduce the efficiency of COD removal from 74.5% to 65.38%, Cd removal from 24.3% to 32.3% and Ni removal 13.8% to 28.5%. Initial metals reduced the efficiency of COD removal at low, middle and high levels by 82.5%, 71.75%, 55.875%, respectively. Initial metals at low, middle, and high levels were obtained Cd removal efficiency of 0%, 52.2%, 32.6% and Ni removal efficiency of 0%, 36.3%, 27%, respectively. Optimal response for COD removal is 68.5% with factor initial metal middle and ratio C/N 50.
机译:本研究重点介绍活性污泥处理由连续反应器进行。 Merriote管容量为10L,排放为10L /天作为入口。在10L体积通气罐旁边,发生生物处理,pH 7±0.2,DO≥3mg/ L是控制变量。用于测试入口和出口的COD,CD和NI。人造废物用作营养比的入口C:N:P为100:5:1。播种阶段发生13天以获得MLSS值≥2000mg/ L.适应I用于将微生物适应环境发生27天和适应性II持续11天,作为重金属的微生物ADA pTation。增加T H E C / N比F RO M 20至50将使COD去除效率从74.5%降低至65.38%,从24.3%的去除率降至32.3%,Ni除去13.8%至28.5%。初始金属将低,中高水平的COD去除效率降低82.5%,分别为71.75%,55.875%。获得低,中间和高水平的初始金属,得到0%,52.2%,32.6%和Ni去除效率分别为0%,36.3%,27%。 COD去除的最佳响应是68.5%,因子初始金属中部和比率C / N 50。

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