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BIOLOGICAL TREATMENT OF GROUNDWATER WITH HIGH NITRATES CONTENT FOR HEXAVALENT CHROMIUM REMOVAL

机译:高硝酸盐含量的地下水的生物处理六价铬含量

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Several methods have been developed in order to tackle the problem of high hexavalent chromium concentrations in groundwater. Among these, physicochemical methods such as chemical oxidation, ion exchange, adsorption through activated carbon, membrane separation, are very often adopted. However all these methods present several disadvantages such as high capital and operational cost, need for management of the chemical sludge, etc. Because of the need to develop cost - effective and more environmentally friendly techniques, biological removal of Cr(VI) have aroused great interest the last few years. Biological systems, such as bio-reduction, bio-accumulation or bio-sorption using living cells have been examined for their chromium removal abilities. The objective of the present study is to evaluate the effectiveness of anoxic-anaerobic biological treatment systems to provide for appreciable hexavalent chromium reduction from groundwater. According to the results of the batch experiments, Cr(VI) removal can be achieved in a fully anoxic-anaerobic system dosed with an external organic carbon source at an influent COD concentration of 200 mg/L. Furthermore the effect of the hydraulic residence time on process performance was assessed through the operation of a series of anoxic-anaerobic sequential batch reactors at different hydraulic residence times. According to the results of the experimental systems, Cr(VI) removal can be achieved in a fully anoxic-anaerobic system dosed with an external organic carbon source at an influent COD concentration of 200 mg/L and operated at a hydraulic residence time of 1.7 d. Under these conditions almost complete Cr(VI) removal can be achieved for initial Cr(VI) groundwater concentration as high as 3000 ug/L. For lower concentrations of external carbon source hexavalent chromium removal is lower and does not exceed 90%. Complete Cr(VI) removal can also be achieved at lower hydraulic residence times as low as 0.6 d, for initial Cr(VI) concentrations equal to 200 ug/L and mixed liquor temperatures greater than 20°C.
机译:已经开发了几种方法,以解决地下水中高六价铬浓度的问题。其中,经常采用这些,经常采用物理化学方法,例如化学氧化,离子交换,通过活性炭,膜分离吸附。然而,所有这些方法都存在若干缺点,例如高资本和运营成本,需要管理化学污泥等。由于需要开发成本效益和更环保的技术,生物去除CR(VI)引起了伟大的兴趣过去几年。已经检查了生物系统,例如使用活细胞的生物减少,生物积累或生物吸附,用于其铬去除能力。本研究的目的是评估缺氧 - 厌氧生物处理系统的有效性,以提供来自地下水的可观六价铬。根据批量实验的结果,可以在用外部有机碳源的完全缺氧 - 厌氧系统中进行Cr(VI)去除,其在200mg / L的流动鳕鱼浓度下。此外的水力停留时间对工艺性能的影响是通过在不同的水力停留时间进行一系列缺氧 - 厌氧顺序间歇反应器的操作进行评估。根据实验系统的结果,铬(VI)的去除可以与在200毫克/升的进水COD浓度的外部有机碳源给药完全缺氧 - 厌氧系统来实现和操作在1.7的水力停留时间天。在这些条件下,几乎完全的Cr(VI)可以去除初始Cr(VI)地下水浓度高达3000ug / L.对于较低浓度的外部碳源六价铬除去较低,不超过90%。结束Cr(VI)除去,还可以在低至0.6d的较低液压停留时间,对于初始Cr(VI)浓度等于200ug / L和大于20℃的混合液温度。

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