Journal of Textile Research ›› 2026, Vol. 47 ›› Issue (04): 52-60.doi: 10.13475/j.fzxb.20251001901

• Fiber Materials • Previous Articles     Next Articles

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 Online:2026-04-15 Published:2026-06-24
  • Contact: WANG Minghuan E-mail:wangmh@zut.edu.cn

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

CLC Number: 

  • TB321

Fig.1

SEM images of PS-based materials. (a) PS/2-methylimidazole; (b) PS/ZIF-67"

Fig.2

FT-IR spectra of PS/ZIF-67, ZIF-67 and PS"

Fig.3

TG curves of PS and PS/ZIF-67"

Fig.4

XRD patterns of ZIF-67 and PS/ZIF-67"

Fig.5

Adsorption-desorption isotherms(a) and pore size distribution(b) of PS/ZIF-67"

Fig.6

Co2p spectrum of PS/ZIF-67"

Fig.7

Degradation processes of different dyes and tetracycline"

Fig.8

Effect of different initia mass concentrations. (a) Degradation processes at different initial concentrations; (b) Corresponding degradation kinetic fitting plot"

Fig.9

Effect of different catalytic systems. (a) Degradation processes of different systems; (b) Corresponding degradation kinetic fitting plot"

Fig.10

Effect of different catalyst dosages. (a) Degradation processes with different catalyst dosages; (b) Corresponding degradation kinetic fitting plot"

Fig.11

Effect of different PMS dosages. (a) Degradation processes with different PMS dosages; (b) Corresponding degradation kinetic fitting plot"

Fig.12

Effect of different temperatures. (a) Degradation processes at different temperatures; (b) Corresponding degradation kinetic fitting plot"

Fig.13

Effect of different pH values. (a) Degradation processes at different pH values;(b) Corresponding degradation kinetic fitting plot"

Fig.14

Identification of key active species in PS/ZIF-67-catalyzed MB degradation. (a) Effect of scavengers on MB degradation; (b) EPR spectra"

Fig.15

Cyclability and practicality of MB degradation by PS/ZIF-67. (a) Reusability; (b) Degradation efficiency in different water matrices"

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