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

机译:在聚酯生产过程中,光芬顿氧化与活性污泥一起分解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 in producing paints and lacquers. The EPA and the International Agency for Research on Cancer(IARC) classified 1,4-dioxane as a GROUP B2(probable human) carcinogen. 1,4-dioxane is also produced as a by-product during the manufacture of polyester. In this research, a polyester manufacturing company (i.e. K Co.) in Gumi, Korea was investigated regarding the release of high concentrations of 1,4-dioxane (about 600 mg/L) and whether treatment prior to release should occur to meet with the level of the regulation standard (e.g., 5 mg/L in 2010). A 10 ton/day pilot-scale treatment system using photo-Fenton oxidation was able to remove approximately 90% of 1,4-dioxane under the conditions that concentrations of 2800 ppm H2O2 and 1,400 ppm FeSO4 were maintained along with 10 UV-C lamps (240 mW/cm2) installed and operated continuously during aeration. However, the effluent concentration of 1,4-dioxane was still high at about 60 mg/L where TOC concentration in the effluent had been moreover increased due to decomposed products such as aldehydes and organic acids. Thus, further investigation is needed to see whether the bench scale (reactor volume, 8.9 L) of activated sludge could facilitate the decomposition of 1,4-dioxane and their by-products (i.e., TOC). As a result, 1,4-dioxane in the effluent has been decreased as low as 0.5 mg/L. The optimal conditions for the activated sludge process that were obtained are as follows: DO, 3-3.5 mg/L; HRT, 24 h; SRT 15 d; MLSS, 3,000 mg/L. Consequently, photo-Fenton oxidation coupled with activated sludge can make it possible to efficiently 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,用作生产油漆和清漆的溶剂。 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。 1,4-二恶烷在聚酯生产过程中也作为副产物生产。在这项研究中,对韩国Gumi的一家聚酯制造公司(即K Co.)进行了调查,研究了其高浓度的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满足法规标准水平(例如,2010年为5 mg / L)。在保持2800 ppm H2O2和1,400 ppm FeSO4的浓度以及10支UV-C灯的条件下,使用光芬顿氧化的10吨/天中试规模处理系统能够去除约90%的1,4-二恶烷。 (240 mW / cm2)在曝气期间连续安装并运行。然而,1,4-二恶烷的废水浓度仍然很高,约为60mg / L,其中由于醛和有机酸等分解产物,废水中的TOC浓度也增加了。因此,需要进一步研究以确定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,废水中的1,4-二恶烷已降低至0.5 mg / L。获得的活性污泥工艺的最佳条件如下:DO,3-3.5 mg / L; HRT,24小时; SRT 15天; MLSS,3,000 mg / L。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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