Volume 14 Issue 4
Jul.  2024
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CHEN Y,NI P F,WU C D,et al.Efficiency and mechanism of microbubble O3/H2O2 advanced treatment of secondary effluent from a resin factory[J].Journal of Environmental Engineering Technology,2024,14(4):1158-1166 doi: 10.12153/j.issn.1674-991X.20240201
Citation: CHEN Y,NI P F,WU C D,et al.Efficiency and mechanism of microbubble O3/H2O2 advanced treatment of secondary effluent from a resin factory[J].Journal of Environmental Engineering Technology,2024,14(4):1158-1166 doi: 10.12153/j.issn.1674-991X.20240201

Efficiency and mechanism of microbubble O3/H2O2 advanced treatment of secondary effluent from a resin factory

doi: 10.12153/j.issn.1674-991X.20240201
  • Received Date: 2024-03-31
  • Aiming at the problem that traditional biodegradation can not degrade the chemical oxygen demand (COD) of benzene series, polyvinyl alcohol and other macromolecular organic compounds in resin wastewater, and can not meet the discharge standard, a microbubble O3/H2O2 system was constructed to treat the secondary effluent of a resin factory deeply. The COD degradation effects of microbubble O3 aeration and ordinary O3 aeration were compared, and the effects of inlet O3 concentration, H2O2 concentration and initial pH on COD degradation efficiency of microbubble O3/H2O2 system were investigated. The mineralization effect of the system was verified by total organic carbon (TOC), and the active substances in microbubble O3/H2O2 were detected by electron paramagnetic resonance spectrometer (EPR). Finally, the types of main organic substances in wastewater before and after degradation were analyzed by GC-MS, and the mechanism and path of COD degradation by microbubble O3/H2O2 system were analyzed. The results showed that: (1) In the microbubble O3/H2O2 system, the particle size of microbubbles was mainly distributed in the range of 10-50 μm, with an average particle size of 32.82 μm. Compared with ordinary aeration, microbubble O3 system had a higher degradation rate of COD, which indicated that microbubbles could prolong the rising time of O3 bubbles, increase the specific surface area of O3 bubbles, and improve the mass transfer coefficient and utilization rate of O3. (2) The analysis of influencing factors of COD degradation by microbubble O3/H2O2 system showed that when O3 concentration was 60 mg/L, H2O2 concentration was 29.37 mmol/L, and pH was 7 after 60 minutes of reaction, the COD degradation rate of secondary effluent of the resin factory by microbubble O3/H2O2 system was 89.53%, and the treated effluent COD was 15.05 mg/L, meeting the requirements of Emission Standard of Pollutants for Synthetic Resin Industry (GB 31572-2015). (3) The EPR test showed that H2O2 could promote the microbubble O3 system to produce more superoxide radicals ($\cdot{\mathrm{O}}_2^- $) and hydroxyl radicals (·OH), thus improving the oxidation capacity of the system and the degradation effect of COD. According to the results of GC-MS, the possible degradation path was inferred. Macromolecules in the secondary effluent from the resin factory, mainly composed of long-chain alkanes and cycloalkanes, underwent chain-breaking and ring-opening by O3, and were mineralized or degraded into micromolecule substances, mainly small-molecule organic acids, under the action of ·OH and other free radicals

     

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  • [1]
    曲岩松. “十四五” 期间中国合成树脂工业的机遇和挑战[J]. 中国塑料,2022,36(3):140-145.

    QU Y S. Opportunities and challenges of China's synthetic resin industry during the 14th Five-Year[J]. China Plastics,2022,36(3):140-145.
    [2]
    环境保护部, 国家质量监督检验检疫总局. 合成树脂工业污染物排放标准: GB 31572—2015[S]. 北京: 中国环境科学出版社, 2015.
    [3]
    薛禹. 催化氧化-生物降解耦合工艺处理离子交换树脂废水[D]. 扬州: 扬州大学, 2023.
    [4]
    高阳顺. 环氧树脂生产废水处理的过程与应用[D]. 郑州: 郑州大学, 2022.
    [5]
    张亮, 周姝岑, 李攀, 等. 电絮凝-微纳米气泡臭氧氧化工艺处理高盐印染废水的研究[J]. 环境工程技术学报,2023,13(2):639-647.

    ZHANG L, ZHOU S C, LI P, et al. Study on treatment of high-salt printing and dyeing wastewater by electroflocculation-micro-nano-bubble ozone oxidation process[J]. Journal of Environmental Engineering Technology,2023,13(2):639-647.
    [6]
    王吉红. 水力空化/臭氧工艺深度处理印染废水及其机理研究[D]. 北京: 北京科技大学, 2023.
    [7]
    LI X, WANG Y J, YUAN S, et al. Degradation of the anti-inflammatory drug ibuprofen by electro-peroxone process[J]. Water Research,2014,63:81-93. doi: 10.1016/j.watres.2014.06.009
    [8]
    LEE Y, GERRITY D, LEE M J, et al. Prediction of micropollutant elimination during ozonation of municipal wastewater effluents: use of kinetic and water specific information[J]. Environmental Science & Technology,2013,47(11):5872-5881.
    [9]
    WANG Y J, YU G, DENG S B, et al. The electro-peroxone process for the abatement of emerging contaminants: mechanisms, recent advances, and prospects[J]. Chemosphere,2018,208:640-654. doi: 10.1016/j.chemosphere.2018.05.095
    [10]
    ZHANG J, LIU M Q, PANG B, et al. Ciprofloxacin degradation in microbubble ozonation combined with electro-generated H2O2 process: operational parameters and oxidation mechanism[J]. Separation and Purification Technology,2023,325:124676. doi: 10.1016/j.seppur.2023.124676
    [11]
    WANG B W, JIAO H, SU H J, et al. Degradation of pefloxacin by hybrid hydrodynamic cavitation with H2O2 and O3[J]. Chemosphere, 2022, 303: 135299.
    [12]
    GU J Y, LI S S, XIE J X, et al. Degradation of atrazine by electro-peroxone enhanced by Fe and N co-doped carbon nanotubes with simultaneous catalysis of H2O2 and O3[J]. Chemosphere,2024,349:140919. doi: 10.1016/j.chemosphere.2023.140919
    [13]
    李天琦. O3/H2O2高级氧化法产生羟基自由基的过程控制研究[D]. 青岛: 青岛大学, 2022.
    [14]
    WANG H, ZHANG S Y, HE X W, et al. Comparison of macro and micro-pollutants abatement from biotreated landfill leachate by single ozonation, O3/H2O2, and catalytic ozonation processes[J]. Chemical Engineering Journal,2023,452:139503. doi: 10.1016/j.cej.2022.139503
    [15]
    邓超, 杨丽, 陈海军, 等. 微纳米气泡发生装置及其应用的研究进展[J]. 石油化工,2014,43(10):1206-1213.

    DENG C, YANG L, CHEN H J, et al. Progresses in research and application of micro-nano bubble generating device[J]. Petrochemical Technology,2014,43(10):1206-1213.
    [16]
    王冠宇, 寇丽红, 刘敏, 等. 微纳米气泡与臭氧催化氧化联用技术的应用进展[J]. 煤质技术,2023,38(4):21-28.

    WANG G Y, KOU L H, LIU M, et al. Application advance of combined technology of Micro-Nano Bubbles and catalytic ozonation[J]. Coal Quality Technology,2023,38(4):21-28.
    [17]
    杜明辉, 王勇, 高群丽, 等. 臭氧微气泡处理有机废水的效果与机制[J]. 化工进展,2021,40(12):6907-6915.

    DU M H, WANG Y, GAO Q L, et al. Mechanism and efficiency of ozone microbubble treatment of organic wastewater[J]. Chemical Industry and Engineering Progress,2021,40(12):6907-6915.
    [18]
    FAN W, AN W G, HUO M X, et al. An integrated approach using ozone nanobubble and cyclodextrin inclusion complexation to enhance the removal of micropollutants[J]. Water Research,2021,196:117039. doi: 10.1016/j.watres.2021.117039
    [19]
    杨旭. 微气泡催化臭氧化降解制药废水过程及机制研究[D]. 石家庄: 河北科技大学, 2022.
    [20]
    陆雨轩, 马永平, 刘晨, 等. 臭氧氧化对印染废水中PVA的氧化效果研究[J]. 环境科学与技术,2022,45(1):108-113.

    LU Y X, MA Y P, LIU C, et al. Study on removal of PVA from textile and dyeing wastewater by ozonation[J]. Environmental Science & Technology,2022,45(1):108-113.
    [21]
    仇欢. 催化臭氧/混凝深度去除化工园区生化尾水中典型有机物研究[D]. 南京: 南京大学, 2019.
    [22]
    刘赛. 臭氧氧化/湿式氧化联用工艺降解PVA纺织材料的研究[D]. 无锡: 江南大学, 2018.
    [23]
    颜鸣扬. O3/H2O2-SBR法对水中青霉素G的去除效能与机理[D]. 长沙: 湖南农业大学, 2020.
    [24]
    程莹, 臧纪, 宋骏杰, 等. 基于臭氧微纳米气泡的O3-H2O2体系降解有机污染物的效能与影响因素[J]. 环境工程技术学报,2022,12(4):1317-1323.

    CHENG Y, ZANG J, SONG J J, et al. Degradation efficiency and influencing factors of organic contaminants in O3-H2O2 system based on ozone micro-nanobubbles[J]. Journal of Environmental Engineering Technology,2022,12(4):1317-1323.
    [25]
    潘海如. 某化工高盐废水膜分离提取硫酸钠研究[D]. 合肥: 安徽建筑大学, 2022.
    [26]
    MALIK S N, GHOSH P C, VAIDYA A N, et al. Hybrid ozonation process for industrial wastewater treatment: principles and applications: a review[J]. Journal of Water Process Engineering,2020,35:101193. doi: 10.1016/j.jwpe.2020.101193
    [27]
    颜鸣扬, 颜智勇, 蔡意祥, 等. O3/H2O2体系降解水中青霉素G的效能及其降解机理[J]. 环境工程学报,2020,14(9):2485-2493.

    YAN M Y, YAN Z Y, CAI Y X, et al. Efficiency and mechanism of penicillin G degradation in water by O3/H2O2 method[J]. Chinese Journal of Environmental Engineering,2020,14(9):2485-2493.
    [28]
    郭金虎, 王树涛. 微气泡O3/H2O2深度处理某化工园区二级出水效能与机制[J]. 哈尔滨工业大学学报,2024,56(2):132-140.

    GUO J H, WANG S T. Efficiency and mechanism of microbubble O3/H2O2 advanced treatment of secondary effluent from a chemical park[J]. Journal of Harbin Institute of Technology,2024,56(2):132-140.
    [29]
    CHENG X, GUO H G, ZHANG Y L, et al. Non-photochemical production of singlet oxygen via activation of persulfate by carbon nanotubes[J]. Water Research,2017,113:80-88. doi: 10.1016/j.watres.2017.02.016
    [30]
    王勇, 杜明辉, 张宁, 等. α-Fe2O3催化臭氧氧化处理苯酚废水的效果及机理[J]. 环境科学研究,2022,35(8):1818-1826.

    WANG Y, DU M H, ZHANG N, et al. Degradation effect and mechanism of phenol wastewater by α-Fe2O3 catalytic ozone oxidation[J]. Research of Environmental Sciences,2022,35(8):1818-1826.
    [31]
    TONG K, ZHANG Y H, LIU G H, et al. Treatment of heavy oil wastewater by a conventional activated sludge process coupled with an immobilized biological filter[J]. International Biodeterioration & Biodegradation,2013,84:65-71. ◇
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