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Decomposition of 1,4-dioxane by photo-Fenton oxidation coupled with activated sludge in a polyester manufacturing process

机译:聚酯制造过程中光芬顿氧化与活性污泥的结合作用分解1,4-二恶烷

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The cyclic ether 1,4-dioxane is a synthetic industrial chemical that is used as a solvent innproducing paints and lacquers. The EPA and the International Agency for Research onnCancer(IARC) classified 1,4-dioxane as a GROUP B2(probable human) carcinogen. 1,4-dioxane isnalso produced as a by-product during the manufacture of polyester. In this research, a polyesternmanufacturing company (i.e. K Co.) in Gumi, Korea was investigated regarding the release of highnconcentrations of 1,4-dioxane (about 600 mg/L) and whether treatment prior to release shouldnoccur to meet with the level of the regulation standard (e.g., 5 mg/L in 2010). A 10 ton/day pilotscalentreatment system using photo-Fenton oxidation was able to remove approximately 90% ofn1,4-dioxane under the conditions that concentrations of 2800ppm H2O2 and 1,400ppm FeSO4nwere maintained along with 10 UV-C lamps (240mW/cm2) installed and operated continuouslynduring aeration. However, the effluent concentration of 1,4-dioxane was still high at aboutn60 mg/L where TOC concentration in the effluent had been moreover increased due tondecomposed products such as aldehydes and organic acids. Thus, further investigation is needednto see whether the bench scale (reactor volume, 8.9 L) of activated sludge could facilitate thendecomposition of 1,4-dioxane and their by-products (i.e., TOC). As a result, 1,4-dioxane in theneffluent has been decreased as low as 0.5 mg/L. The optimal conditions for the activated sludgenprocess that were obtained are as follows: DO, 3-3.5 mg/L; HRT, 24 h; SRT 15 d; MLSS, 3,000 mg/L.nConsequently, photo-Fenton oxidation coupled with activated sludge can make it possible tonefficiently decompose 1,4-dioxane to keep up with that of the regulation standard.
机译:环状醚1,4-二恶烷是一种合成工业化学品,用作产生油漆和清漆的溶剂。 EPA和国际癌症研究机构(IARC)将1,4-二恶烷列为B2组(可能是人类)致癌物。 1,4-二恶烷也是在聚酯生产过程中的副产品。在这项研究中,对韩国龟尾市的一家聚酯制造公司(即K Co.)进行了调查,以研究其高浓度的1,4-二恶烷(约600 mg / L)的释放以及释放前是否应进行处理以使其达到法规标准(例如,2010年为5 mg / L)。在保持2800ppm H2O2和1400ppm FeSO4n的浓度以及安装10支UV-C灯(240mW / cm2)的条件下,采用光芬顿氧化的10吨/天中规模氧化处理系统能够去除大约90%的n1,4-二恶烷。并持续进行曝气。然而,1,4-二恶烷的废水浓度仍然很高,约为60 mg / L,其中废水中的总有机碳浓度由于醛和有机酸等被吨分解的产物而增加。因此,需要进一步研究以查看活性污泥的工作台规模(反应器体积为8.9 L)是否可以促进1,4-二恶烷及其副产物(即TOC)的分解。结果,流出物中的1,4-二恶烷已降低至0.5 mg / L。获得的活性污泥处理的最佳条件如下:DO,3-3.5 mg / L; HRT,24小时; SRT 15天; MLSS,3,000 mg / L.n因此,光芬顿氧化与活性污泥相结合可以有效地分解1,4-二恶烷,以符合法规标准。

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