纺织学报 ›› 2026, Vol. 47 ›› Issue (07): 10-18.doi: 10.13475/j.fzxb.20260405701

• 第二十八届中国科协年会学术论文·减污降碳共性技术突破专栏· • 上一篇    下一篇

聚四氟乙烯中空纤维膜接触反应器中臭氧传质强化及其应用性能

杨帆1,2, 崔松松3, 王姗丽4, 王振华1,2, 戴高奇1,2, 余德游1,2()   

  1. 1 浙江理工大学 生物基纤维材料全国重点实验室, 浙江 杭州 310018
    2 浙江理工大学 生态染整技术教育部工程研究中心, 浙江 杭州 310018
    3 浙江科峰有机硅股份有限公司, 浙江 嘉兴 314423
    4 浙江纺织服装职业技术学院, 浙江 宁波 315211
  • 收稿日期:2026-04-27 修回日期:2026-05-14 出版日期:2026-07-15 发布日期:2026-07-29
  • 通讯作者: 余德游(1992—),男,副教授。主要研究方向为纺织印染绿色制造。E-mail:yudeyou92@zstu.edu.cn
  • 作者简介:杨帆(2000—),女,硕士生。主要研究方向为膜接触臭氧反应器在印染废水处理中的应用。
  • 基金资助:
    国家自然科学基金面上项目(22476183);浙江省重点研发计划项目(2026C02A1004)

Enhancement of ozone mass transfer in polytetrafluoroethylene hollow fiber membrane contactor reactor and its application performance

YANG Fan1,2, CUI Songsong3, WANG Shanli4, WANG Zhenhua1,2, DAI Gaoqi1,2, YU Deyou1,2()   

  1. 1 State Key Laboratory of Bio-based Fiber Materials, Zhejiang Sci-Tech University, Hangzhou, Zhejiang 310018, China
    2 Engineering Research Center of Ecological Dyeing and Finishing Technology (Ministry of Education), Zhejiang Sci-Tech University, Hangzhou, Zhejiang 310018, China
    3 Zhejiang Kefeng Silicone Co., Ltd., Jiaxing, Zhejiang 314423, China
    4 Zhejiang Fashion Institute of Technology, Ningbo, Zhejiang 315211, China
  • Received:2026-04-27 Revised:2026-05-14 Published:2026-07-15 Online:2026-07-29

摘要:

针对传统鼓泡曝气方式存在的臭氧(O3)传质效率低、利用率不足的瓶颈问题,采用聚四氟乙烯(PTFE)中空纤维膜构建膜接触反应器(MCR),实现O3气体无泡传质。系统对比分析了疏水膜、亲水膜及传统曝气3种O3传质方式的性能差异,考察了进水流量、进气流量、进气质量浓度及液相初始pH值等工艺参数对液相O3平衡质量浓度及表观传质系数的影响规律,并评估优化工艺条件对真实印染废水的深度处理效果。结果表明:疏水PTFE中空纤维膜在各种工艺条件下均表现出最优的O3传质性能。在疏水PTFE中空纤维膜MCR体系中,增大进水流量可减薄液膜边界层、提升传质系数,但会缩短接触时间、降低液相O3平衡质量浓度;最优进气流量为100 mL/min,且在进气质量浓度为67.7 mg/L时O3气体传质效果最佳;当溶液初始pH值为7时,传质推动力与O3稳定性达到最佳平衡。在进水流量为146.67 mL/min、进气流量为100 mL/min、进气质量浓度为67.7 mg/L、初始pH值为7的工艺条件下,疏水膜、亲水膜和传统曝气3种传质方式获得的最大表观传质系数分别为0.623、0.341和0.602 min-1。疏水膜对真实印染废水COD的去除率达60.7%、单位臭氧COD去除量为0.119 mg/mg,分别是传统曝气的4倍和3.8倍,展现出较好的印染废水处理应用潜力。

关键词: 聚四氟乙烯, 中空纤维膜, 膜接触反应器, O3氧化, 印染废水, 传质效率, 废水处理

Abstract:

Objective Conventional bubble aeration suffers from low ozone mass transfer efficiency and insufficient ozone utilization, which limits the practical application of ozonation in the advanced treatment of printing and dyeing wastewater. Membrane contactor reactors provide a stable gas-liquid interface for bubbleless ozone transfer and offer a promising strategy to overcome the intrinsic limitations of bubble-based aeration. A polytetrafluoroethylene (PTFE) hollow fiber membrane contactor reactor was constructed to enhance ozone mass transfer, and the mass transfer behavior and wastewater treatment performance of hydrophobic PTFE membrane, hydrophilic PTFE membrane, and conventional aeration were systematically compared.

Method Commercial hydrophobic and hydrophilic PTFE hollow fiber membranes were adopted to construct membrane contactor reactors, while a conventional aerator was used as the control. The surface morphologies of the membranes were characterized by scanning electron microscopy. Ozone mass transfer experiments were carried out under different influent flow rates, inlet gas flow rates, inlet ozone mass concentrations, and initial liquid-phase pH values. The equilibrium dissolved ozone concentration and apparent volumetric mass transfer coefficient (KLa) were calculated based on a pseudo-first-order mass transfer model. Under the optimized operating conditions, the hydrophobic PTFE hollow fiber membrane contactor was further applied to the advanced treatment of actual printing and dyeing wastewater, and its chemical oxygen demand (COD) removal efficiency and ozone utilization efficiency were evaluated.

Results The hydrophobic PTFE hollow fiber membrane exhibited the best ozone mass transfer performance among the three transfer modes under the investigating conditions. Increasing the influent flow rate led to the thinning of the boundary layer and improved the mass transfer coefficient, but excessive flow shortened the gas-liquid contact time and reduced the equilibrium dissolved ozone concentration. The optimal gas flow rate and inlet ozone mass concentration were determined to be 100 mL/min and 67.7 mg/L, respectively. The initial pH value was also found to strongly affect ozone transfer and stability, with pH=7 providing the best balance between mass transfer driving force and ozone decomposition. Under the optimized conditions of influent flow rate of 146.67 mL/min, gas flow rate of 100 mL/min, inlet ozone mass concentration of 67.7 mg/L, and initial pH value of 7, the maximum KLa values of the hydrophobic membrane, hydrophilic membrane, and conventional aerator were 0.623, 0.341, and 0.602 min-1, respectively. For printing and dyeing wastewater treatment, the COD removal rate achieved by the hydrophobic PTFE membrane reached 60.7%, which was approximately 4 times that of the conventional aerator. The COD removal per unit ozone consumption reached 0.119 mg/mg, about 3.8 times that of conventional aerator.

Conclusion The hydrophobic PTFE hollow fiber membrane contactor effectively enhances ozone mass transfer by maintaining a stable bubbleless gas-liquid interface and reducing liquid-side mass transfer resistance. Compared with hydrophilic membrane contact and conventional bubble aeration, the hydrophobic membrane shows higher mass transfer efficiency, better ozone utilization, and superior COD removal performance in actual printing and dyeing wastewater treatment. This study provides a feasible technical route for improving ozone utilization efficiency and promoting the engineering application of membrane contactor-assisted ozonation in textile wastewater treatment.

Key words: polytetrafluoroethylene, hollow fiber membrane, membrane contactor reactor, ozone oxidation, printing and dyeing wastewater, mass transfer efficiency, wastewater treatment

中图分类号: 

  • TS973.1

图1

实验装置示意图"

图2

不同放大倍数下PTFE中空纤维膜的SEM照片"

图3

进水流量对液相O3质量浓度的影响"

表1

进水流量对传质系数的影响"

进水流量/
(mL·min-1)
KLa/min-1
疏水膜 亲水膜
80 0.231 0.098
120 0.242 0.154
146.67 0.272 0.172
173.33 0.276 0.148

图4

进气流量对液相O3质量浓度的影响"

表2

进气流量对传质系数的影响"

进气流量/
(mL·min-1)
KLa/min-1
传统曝气头 疏水膜 亲水膜
30 0.086 0.089 0.079
55 0.106 0.250 0.183
75 0.313 0.267 0.231
100 0.435 0.478 0.261
200 0.426 0.344 0.256

图5

进气质量浓度对液相O3质量浓度的影响"

表3

进气质量浓度对传质系数的影响"

进气质量
浓度/(mg·L-1)
KLa/min-1
传统曝气头 疏水膜 亲水膜
50 0.381 0.384 0.186
63.5 0.435 0.534 0.273
67.7 0.602 0.623 0.341
68.3 0.569 0.489 0.325

图6

液相初始pH值对液相O3质量浓度的影响"

表4

液相初始pH值对传质系数的影响"

pH值 KLa/min-1
传统曝气头 疏水膜
3 0.205 0.289
5 0.224 0.295
7 0.602 0.623
9 0.326 0.347
11

图7

疏水膜与传统曝气头对实际印染废水中COD去除效果的对比"

[1] ZHANG J, YANG L, WANG Z, et al. A highly permeable loose nanofiltration membrane prepared via layer assembled in-situ mineralization[J]. Journal of Membrane Science, 2019, 587: 117159.
doi: 10.1016/j.memsci.2019.05.083
[2] 唐政坤, 刘艳缤, 徐晨烨, 等. 面向减污降碳目标的纺织工业环境治理发展趋势[J]. 纺织学报, 2022, 43(1): 131-140.
TANG Zhengkun, LIU Yanbin, XU Chenye, et al. Trend of environmental governance in textile industry aiming at carbon neutrality and emission reduction[J]. Journal of Textile Research, 2022, 43(1): 131-140.
[3] WANG J, CHEN H. Catalytic ozonation for water and wastewater treatment: recent advances and perspective[J]. Science of The Total Environment, 2020, 704: 135249.
doi: 10.1016/j.scitotenv.2019.135249
[4] YAN Y, FOTIDIS I A, FU D, et al. Can ozone mass transfer in water treatment be enhanced through independent pressurized ozonation?[J]. Journal of Environmental Chemical Engineering, 2024, 12(5): 113714.
doi: 10.1016/j.jece.2024.113714
[5] 汪文强, 高鹏贺, 季献华, 等. E-H2O2耦合O3深度处理苯胺和硝基苯废水研究[J]. 水处理技术, 2025, 51(5): 132-137, 142.
doi: 10.16796/j.cnki.1000-3770.2025.05.022
WANG Wenqiang, GAO Penghe, JI Xianhua, et al. Advanced treatment of aniline and nitrobenzene wastewater by E-H2O2 coupled O3[J]. Technology of Water Treatment, 2025, 51(5): 132-137, 142.
doi: 10.16796/j.cnki.1000-3770.2025.05.022
[6] 秦月娇, 焦纬洲, 杨鹏飞, 等. 强化臭氧传质的研究进展[J]. 过程工程学报, 2017, 17(2): 420-426.
doi: 10.12034/j.issn.1009-606X.216292
QIN Yuejiao, JIAO Weizhou, YANG Pengfei, et al. Research progress of enhancement of ozone mass transfer[J]. The Chinese Journal of Process Engineering, 2017, 17(2): 420-426.
doi: 10.12034/j.issn.1009-606X.216292
[7] SUN D, WANG Y, LIU B, et al. Study on the efficiency and mechanism of ozone micro-nano bubble system degradation of Geosmin[J]. Desalination and Water Treatment, 2025, 321: 100922.
doi: 10.1016/j.dwt.2024.100922
[8] DUAN Y, ZHAO D, LIU Z, et al. Hydrogen peroxide enhancing the process of MnO2-modified ceramic membrane catalyzing micro-nano bubble[J]. Separation and Purification Technology, 2025, 353: 128320.
doi: 10.1016/j.seppur.2024.128320
[9] CHEN X, WANG X, LI Y, et al. Bubbleless membrane contactor for enhanced ozone mass transfer and ozonation for water purification[J]. Separation and Purification Technology, 2024, 349: 127823.
doi: 10.1016/j.seppur.2024.127823
[10] YIN Y, LIU Q, XIAO M, et al. Enhancing CO2 capture performance by changing membrane fiber arrangement in multi-fiber membrane contactors[J]. Journal of Environmental Chemical Engineering, 2025, 13(2): 115562.
doi: 10.1016/j.jece.2025.115562
[11] SHIN J, MERLE T, COCKX A, et al. Ozonation of wastewater effluent by the MEMBRO3X contactor: Micropollutants abatement and bromate mitigation[J]. Water Research, 2025, 283: 123853.
doi: 10.1016/j.watres.2025.123853
[12] 刘劲扬, 李成才, 朱海霖, 等. 非对称结构聚四氟乙烯中空管式纤维膜的制备及油水分离性能[J]. 纺织学报, 2025, 46(12): 11-18.
LIU Jinyang, LI Chengcai, ZHU Hailin, et al. Preparation and oil-water separation performance of asymmetric structure polytetrafluoroethene empty tube fiber membrane[J]. Journal of Textile Research, 2025, 46(12): 11-18.
[13] 李成才, 朱登辉, 朱海霖, 等. 聚四氟乙烯膜的超疏水改性及应用研究进展[J]. 纺织学报, 2024, 45(8): 65-71.
LI Chengcai, ZHU Denghui, ZHU Hailin, et al. Research progress of superhydrophobic modification and application of polytetrafluoroethylene membrane[J]. Journal of Textile Research, 2024, 45(8): 65-71.
[14] BEIN E, ZUCKER I, DREWES J E, et al. Ozone membrane contactors for water and wastewater treatment: a critical review on materials selection, mass transfer and process design[J]. Chemical Engineering Journal, 2021, 413: 127393.
doi: 10.1016/j.cej.2020.127393
[15] ATCHARIYAWUT S, PHATTARANAWIK J, LEIKNES T, et al. Application of ozonation membrane contacting system for dye wastewater treatment[J]. Separation and Purification Technology, 2009, 66(1): 153-158.
doi: 10.1016/j.seppur.2008.11.011
[16] 卢凤华, 陈滢, 刘敏, 等. 靛蓝二磺酸钠分光光度法和碘滴定法测定水中臭氧含量适用条件的比较[J]. 理化检验(化学分册), 2014, 50(6): 778-780.
LU Fenghua, CHEN Ying, LIU Min, et al. Comparison of applicability of indigo disulfonate spectrophotometry and iodometric titration for determination of ozone content in water[J]. Physical Testing and Chemical Analysis (Chemical Analysis Section), 2014, 50(6): 778-780.
[17] SCHMITT A, MENDRET J, BROSILLON S. Evaluation of an ozone diffusion process using a hollow fiber membrane contactor[J]. Chemical Engineering Research and Design, 2022, 177: 291-303.
doi: 10.1016/j.cherd.2021.11.002
[18] 姚福春, 毕莹莹, 刘超, 等. 膜传质强化催化臭氧氧化技术的研究与机理分析[J]. 现代化工, 2024, 44(9): 86-91.
doi: 10.16606/j.cnki.issn0253-4320.2024.09.017
YAO Fuchun, BI Yingying, LIU Chao, et al. Research and mechanism analysis on membrane mass transfer enhanced catalytic ozonation technology[J]. Modern Chemical Industry, 2024, 44(9): 86-91.
doi: 10.16606/j.cnki.issn0253-4320.2024.09.017
[19] PRADA-VÁSQUEZ M A, PITUCO M M, CAIXETA M P, et al. Ozonation using a stainless-steel membrane contactor: gas-liquid mass transfer and pharmaceuticals removal from secondary-treated municipal wastewater[J]. Chemosphere, 2024, 349: 140888.
doi: 10.1016/j.chemosphere.2023.140888
[20] HERRMANN S, PADLIGUR M C, BIENECK C J, et al. Modeling of tubular membrane contactors for ozonation of water reveals reduced bromate formation with static mixers[J]. Chemical Engineering Science, 2024, 291: 119924.
doi: 10.1016/j.ces.2024.119924
[21] 钱媛媛, 王永杰, 杨雪晶. 臭氧相关水处理工艺及其传质特征研究进展[J]. 化工进展, 2021, 40(S1):411-425.
doi: 10.16085/j.issn.1000-6613.2021-0416
QIAN Yuanyuan, WANG Yongjie, YANG Xuejing. Application of ozone for water treatment and implication of mass transfer characteristics[J]. Chemical Industry and Engineering Progress, 2021, 40(S1): 411-425.
doi: 10.16085/j.issn.1000-6613.2021-0416
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