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Decontamination Industrial Pharmaceutical Wastewater By Combining Solar Photo-fen Ton And Biological Treatment

机译:太阳能光粉与生物处理相结合净化工业制药废水

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Characterization and treatment of a real pharmaceutical wastewater containing 775 mg dissolved organic carbon per liter by a solar photo-Fenton/biotreatment were studied. There were also many inorganic compounds present in the matrix. The most important chemical in this wastewater was nalidixic acid (45 mg/L), an antibiotic pertaining to the quinolone group. A Zahn-Wellens test demonstrated that the real bulk organic content of the wastewater was biodegradable, but only after long biomass adaptation; however, the nalidixic acid concentration remained constant, showing that it cannot be biodegraded. An alternative is chemical oxidation (photo-Fenton process) first to enhance biodegradability, followed by a biological treatment (Immobilized Biomass Reactor - IBR). In this case, two studies of photo-Fenton treatment of the real wastewater were performed, one with an excess of H_2O_2 (kinetic study) and another with controlled H_2O_2 dosing (biodegradability and toxicity studies). In the kinetic study, nalidixic acid completely disappeared after 190 min. In the other experiment with controlled H_2O_2, nalidixic acid degradation was complete at 66 mM of H_2O_2 consumed. Biodegradability and toxicity bioassays showed that photo-Fenton should be performed until total degradation of nalidixic acid before coupling a biological treatment. Analysis of the average oxidation state (AOS) demonstrated the formation of more oxidized intermediates. With this information, the photo-Fenton treatment time (190 min) and H_2O_2 dose (66 mM) necessary for adequate biodegradability of the wastewater could be determined. An IBR operated in batch mode was able to reduce the remaining DOC to less than 35 mg/L. Ammonium consumption and NO_3~- generation demonstrated that nitrification was also attained in the IBR. Overall DOC degradation efficiency of the combined photo-Fenton and biological treatment was over 95%, of which 33% correspond to the solar photochemical process and 62% to the biological treatment.
机译:研究了通过太阳光Fenton /生物处理法对每升含775 mg溶解有机碳的实际制药废水的表征和处理。基质中还存在许多无机化合物。该废水中最重要的化学物质是萘啶酸(45 mg / L),属于喹诺酮类抗生素。 Zahn-Wellens试验表明,废水中的实际总有机物含量是可生物降解的,但只有经过长期的生物量适应才能实现。然而,萘啶酸的浓度保持恒定,表明它不能被生物降解。另一种选择是先进行化学氧化(光芬顿法)以增强生物降解能力,然后进行生物处理(固定化生物质反应器-IBR)。在这种情况下,进行了两项用光芬顿处理实际废水的研究,一项是过量的H_2O_2(动力学研究),另一项是受控的H_2O_2剂量(生物降解性和毒性研究)。在动力学研究中,萘啶酸在190分钟后完全消失。在另一个控制H_2O_2的实验中,萘啶酸的降解在消耗66 mM的H_2O_2时完成。生物降解性和毒性生物测定表明,在联用生物处理之前,应进行光芬顿直至萘啶酸完全降解。平均氧化态(AOS)的分析表明形成了更多的氧化中间体。利用该信息,可以确定光-芬顿处理时间(190分钟)和废水的充分生物降解性所需的H_2O_2剂量(66 mM)。以批处理模式运行的IBR能够将剩余的DOC降至35 mg / L以下。铵的消耗和NO_3-的产生表明在IBR中也达到了硝化作用。光芬顿和生物处理相结合的总DOC降解效率超过95%,其中33%对应于太阳光化学过程,而62%对应于生物处理。

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