首页> 外文会议>Biennial conference of the International Association on Water Quality >ANAEROBIC/AEROBIC BIODEGRADATION OF PENTACHLOROPHENOL USING GAC FLUIDIZED BED REACTORS: OPTIMIZATION OF THE EMPTY BED CONTACT TIME
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ANAEROBIC/AEROBIC BIODEGRADATION OF PENTACHLOROPHENOL USING GAC FLUIDIZED BED REACTORS: OPTIMIZATION OF THE EMPTY BED CONTACT TIME

机译:GAC流化床反应器对五氯酚进行厌氧/好氧生物降解:空床接触时间的优化

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An integrated reactor system has been developed to remediate pentachlorophenol (PCP) containing wastes using sequential anaerobic and aerobic biodegradation. Anaerobically, PCP was degraded to approximately equimolar concentrations (>99%) of chlorophenol (CP) in a granular activated carbon (GAC) fluidized bed reactor (FBR) at empty bed contact times (EBCTs) ranging from 18.6 to 2.3 hr. However, at lower EBCTs, chlorophenol concentrations decreased to less than 10% of the influent PCP concentration. The optimal EBCT was determined to be 2.3 hr based on PCP conversion to CPs and stable reactor operation. Decreasing the EBCT fourfold did not inhibit degradation of PCP and its intermediates, and thus, removal of PCP is possible at lower detention times providing a significant cost advantage.Analytical grade PCP was fed via syringe pumps into a GAC FBR at an influent concentration of 200 mg/L. Acting as the primary substrate, ethanol was also fed at a concentration of 1388 mg/L. Effluent PCP and chlorinated phenolic compounds were analyzed weekly to evaluate reactor performance. Biodegradation pathways were also identified. 3-chlorophenol (3-CP) was the predominant CP. Concentrations of 3-CP follow the same trends as 3,5-dichlorophenol (DCP) concentrations. In a similar manner, 4-chlorophenol concentrations correlate with 3,4-DCP concentrations.A second stage aerobic GAC FBR was added after the anaerobic bioreactor which removed the remaining CP and phenols. No phenol or CP has been observed in the effluent or on the GAC. Overall, the influent chemical oxygen demand (COD) loading was reduced from 34 g/L~*d to less than 1.36 g/L~*d.
机译:已开发出一种综合反应器系统,用于通过顺序厌氧和好氧生物降解来修复含有五氯苯酚(PCP)的废物。厌氧地,在颗粒状活性炭(GAC)流化床反应器(FBR)中,PCP在空床接触时间(EBCT)为18.6到2.3小时的范围内降解为大约等摩尔浓度(> 99%)的氯酚(CP)。但是,在较低的EBCT下,氯酚浓度降至进水PCP浓度的10%以下。基于PCP转化为CP和稳定的反应器运行,确定最佳EBCT为2.3小时。将EBCT降低四倍不会抑制PCP及其中间体的降解,因此,可以在更短的保留时间内去除PCP,从而提供显着的成本优势。 分析型五氯苯酚通过注射泵以200 mg / L的进水浓度进料到GAC FBR中。作为主要底物,乙醇也以1388 mg / L的浓度进料。每周对废水中的五氯苯酚和氯化酚类化合物进行分析,以评估反应堆的性能。还确定了生物降解途径。 3-氯苯酚(3-CP)是主要的CP。 3-CP的浓度遵循与3,5-二氯苯酚(DCP)浓度相同的趋势。以类似的方式,4-氯苯酚浓度与3,4-DCP浓度相关。 在厌氧生物反应器之后添加第二阶段好氧GAC FBR,以去除残留的CP和酚。在废水或GAC中未观察到苯酚或CP。总的来说,进水化学需氧量(COD)从34 g / L〜* d降低到小于1.36 g / L〜* d。

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