纺织学报 ›› 2026, Vol. 47 ›› Issue (04): 52-60.doi: 10.13475/j.fzxb.20251001901

• 纤维材料 • 上一篇    下一篇

聚苯乙烯/ZIF-67纳米纤维的制备及其高级氧化降解应用

郭正, 张贺凯, 宋云飞, 朱怡雷, 李佳颍, 郑佳悦, 王明环()   

  1. 中原工学院 智能纺织与织物电子学院, 河南 郑州 450007
  • 收稿日期:2025-10-14 修回日期:2025-12-26 出版日期:2026-04-15 发布日期:2026-06-24
  • 通讯作者: 王明环(1986—),男,讲师,博士。主要研究方向为功能纤维的制备及应用。E-mail: wangmh@zut.edu.cn
  • 作者简介:郭正(1981—),男,副教授,博士。主要研究方向为功能纤维的制备及应用。
  • 基金资助:
    河南省科技攻关项目(242102230019);中国纺织品工业联合会科技指导性计划项目(2020011);中国纺织品工业联合会科技指导性计划项目(2022007)

Preparation and advanced oxidative degradation applications of polystyrene/ZIF-67 nanofibers

GUO Zheng, ZHANG Hekai, SONG Yunfei, ZHU Yilei, LI Jiaying, ZHENG Jiayue, WANG Minghuan()   

  1. College of Intelligent Textiles and Fabric Electronics, Zhongyuan University of Technology, Zhengzhou, Henan 450007, China
  • Received:2025-10-14 Revised:2025-12-26 Published:2026-04-15 Online:2026-06-24

摘要:

为解决水体有机污染物的高效降解问题,以聚苯乙烯(PS)和ZIF-67为原料,通过静电纺丝结合后处理法制备PS/ZIF-67纳米纤维复合材料。采用扫描电子显微镜、傅里叶变换红外光谱、热重分析及N2吸附-脱附等手段对材料性能进行表征,并考察其在过氧硫酸盐体系中对亚甲基蓝的催化降解性能。结果表明:ZIF-67立方体晶相均匀负载于聚苯乙烯纤维表面,成功制备了PS/ZIF-67,其比表面积为7.53 m2/g,平均孔径为28.07 nm。在最优条件(催化剂0.03 g、过硫酸氢钾 0.05 g、pH = 7、温度为25 ℃)下,对50 mg/L亚甲基蓝的降解速率常数达0.189 min-1,30 min内降解率超89%,且经5次循环后降解效率仍保持80%以上。该材料通过活化过硫酸盐产生硫酸根自由基实现对染料的高效降解,为水体有机污染治理用新材料开发提供思路。

关键词: 金属有机框架材料, 聚苯乙烯, ZIF-67, 催化, 亚甲基蓝, 过硫酸盐, 高级氧化工艺, 废水处理

Abstract:

Objective Toxic and persistent organic pollutants (e.g., methylene blue, MB) in water pose a severe threat to ecological safety and human health, and the efficient degradation of such pollutants has long been a tough challenge. To address this issue as well as the drawbacks of poor stability and low recyclability associated with single-phase catalysts, this study aims to fabricate polystyrene(PS)/ZIF-67 nanofiber composites. The catalytic performance of these composites in degrading MB through a peroxymonosulfate-based advanced oxidation system will be systematically evaluated, thereby providing a novel and practical material strategy for organic water pollution control.

Method Using PS powder and ZIF-67 precursor as raw materials, PS/ZIF-67 composite nanofibers were prepared via two steps, i.e., electrospinning of PS fiber (18 kV, 15 cm collector distance, 1.0 mL/h injection rate) and PS fiber post-treatment for in-situ ZIF-67 growth. The fabricated materials were comprehensively characterized by SEM, FT-IR, TG, XRD, and N2 adsorption-desorption (morphology, structure, thermal stability), and their dye-degradation performance (e.g., methylene blue) in PMS system was tested under varied conditions (catalyst/PMS dosage, pH, temperature).

Results ZIF-67 cubic crystals were uniformly loaded onto the surface of polystyrene fibers via in-situ growth, successfully forming PS/ZIF-67 composite materials with a well-defined core-shell structure. Comprehensive characterizations, including N2 adsorption-desorption, XRD, and TG, revealed that the composite possessed a specific surface area of 7.53 m2/g and an average pore diameter of 28.07 nm, presenting a typical mesoporous structure. This porous feature facilitates the diffusion of reactants (e.g., methylene blue, MB) and the exposure of active sites, laying a structural foundation for efficient catalysis. Compared with pure PS fibers, PS/ZIF-67 fibers exhibited significantly enhanced thermal stability with a weight loss rate reduced by about 30% at 400 - 600 ℃, as determined by TG analysis, which prevents structural collapse during catalytic reactions and ensures long-term operational reliability. Under the optimized reaction conditions (0.03 g catalyst dosage, 0.05 g peroxymonosulfate (PMS) dosage, neutral pH=7, and ambient temperature of 25 ℃), the degradation rate constant of 50 mg/L MB reached 0.189 min-1, and the degradation efficiency exceeded 89% within 30 min, outperforming many reported MOF-based composites in similar systems. The composite also exhibited broad potential applicability. It could effectively degrade other typical pollutants, such as methyl orange (a cationic dye, about 76% degradation in 30 min) and tetracycline (an antibiotic, about 68% degradation in 30 min), demonstrating its potential for multi-pollutant water treatment. The composite maintained good cyclic stability, where after 5 consecutive catalytic cycles (each involving centrifugation, washing with deionized water, and drying at 60 ℃), its MB degradation efficiency still remained over 80%, indicating minimal loss of active sites. Kinetic analysis further confirmed that the MB degradation process followed pseudo-first-order kinetics (R2 > 0.99), suggesting a consistent reaction pathway dominated by either radical oxidation or electron transfer. Additional parameter-dependent studies showed that lower initial MB concentrations (≤50 mg/L), appropriate PMS dosage (0.05 g, to avoid excessive radical quenching), and neutral pH (pH=7, optimizing catalyst surface charge) were more conducive to improving the catalytic efficiency of PS/ZIF-67.

Conclusion In this study, PS/ZIF-67 nanofiber composites, integrating PS's fibrous framework and ZIF-67's cubic phase, exhibit typical mesoporous structure (specific surface area= 7.53 m2/g, pore diameter = 28.07 nm), enhanced thermal stability, excellent MB degradation (0.189 min-1, >89% in 30 min under optimal conditions), broad applicability to other pollutants, and good cyclic stability (>80% after 5 cycles) due to improved structural stability and retained active sites. This study supports MOFs-based composites for water decontamination, though coexisting ions in real water limit performance. Future research should explore interference mechanisms and optimize the material to boost anti-interference ability, promoting practical application.

Key words: metal-organic framework, polystyrene, ZIF-67, catalysis, methylene blue, peroxymonosulfate, advanced oxidation processes, wasterwater treatment

中图分类号: 

  • TB321

图1

PS基材料的SEM照片"

图2

PS/ZIF-67、ZIF-67和PS的红外光谱图"

图3

PS和PS/ZIF-67热重曲线图"

图4

ZIF-67和PS/ZIF-67的XRD谱图"

图5

PS/ZIF-67的吸附-脱附等温曲线和孔径分布图"

图6

PS/ZIF-67的Co2p图谱"

图7

不同染料及四环素的降解过程"

图8

不同初始质量浓度的影响"

图9

不同催化体系的影响"

图10

不同催化剂投加量的影响"

图11

不同PMS添加量的影响"

图12

不同温度的影响"

图13

不同pH值下影响"

图14

PS/ZIF-67催化降解亚甲基蓝关键活性物质识别"

图15

PS/ZIF-67对MB降解过程的循环及实用性"

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