Abstract

As the demand for textile products and synthetic dyes increases with the growing global population, textile dye wastewater is becoming one of the most significant water pollution contributors. Azo dyes represent 70% of dyes used worldwide, and are hence a significant contributor to textile waste. In this work, the removal of a reactive azo dye (Reactive Orange 16) from water by adsorption with chitosan grafted poly(poly(ethylene glycol) methyl ether methacrylate) (CTS-GMA-g-PPEGMA) was investigated. The chitosan (CTS) was first functionalized with glycidyl methacrylate and then grafted with poly(poly(ethylene glycol) methyl ether methacrylate) using a nitroxide-mediated polymerization grafting to approach. Equilibrium adsorption experiments were carried out at different initial dye concentrations and were successfully fitted to the Langmuir and Freundlich adsorption isotherm models. Adsorption isotherms showed maximum adsorption capacities of CTS-g-GMA-PPEGMA and chitosan of 200 mg/g and 150 mg/g, respectively, while the Langmuir equations estimated 232 mg/g and 194 mg/g, respectively. The fundamental assumptions underlying the Langmuir model may not be applicable for azo dye adsorption, which could explain the difference. The Freundlich isotherm parameters, n and K, were determined to be 2.18 and 17.7 for CTS-g-GMA-PPEGMA and 0.14 and 2.11 for chitosan, respectively. An “n” value between one and ten generally indicates favorable adsorption. The adsorption capacities of a chitosan-PPEGMA 50/50 physical mixture and pure PPEGMA were also investigated, and both exhibited significantly lower adsorption capacities than pure chitosan. In this work, CTS-g-GMA-PPEGMA proved to be more effective than its parent chitosan, with a 33% increase in adsorption capacity.

Highlights

  • As the discharge of environmental pollutants in receiving waters continues to be a serious concern across the globe, it is important to develop effective approaches for their removal

  • CTS-g-glycidyl methacrylate (GMA)-PPEGMA increased the adsorption capacity by 33% according to the adsorption isotherm data, indicating that CTS-g-GMA-PPEGMA could be an effective adsorbent

  • Experimental data for pure PPEGMA did not fit either of the isotherm models, which would be consistent with observation that pure PPEGMA exhibited negligible adsorption capacity for RO16

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Summary

Introduction

As the discharge of environmental pollutants in receiving waters continues to be a serious concern across the globe, it is important to develop effective approaches for their removal. 40% in the removal of reactive azo dyes [5] These studies would suggest that with tailored (TPP) crosslinked improved the adsorption capacity of chitosan by. 40% in side the removal of reactive azo efficiency dyes [5] These studiescan would suggest that with tailored polymeric chains, the adsorption of chitosan be improved extensively through functionalization. The grafting objectivewas wasachieved to examine adsorption capacity of CTS‐g‐GMA‐PPEGMA through polymer via the nitroxide-mediated polymerization and a graftingfor to RO16 relative to pure chitosan in water for textile wastewater treatment applications. The objective was to examine the adsorption capacity of CTS-g-GMA-PPEGMA for work describes the synthesis and application of PPEGMA‐grafted chitosan for the removal of RO16 relative to pure chitosan in water for textile wastewater treatment applications.

Materials
Instrumentation
Synthesis of CTS-g-GMA
Synthesis of CTS-GMA-g-PPEGMA via Grafting to Approach
Dye Adsorption Experiments
CTS‐g‐GMA
PPEGMA
CTS‐g‐GMA‐PPEGMA
Langmuir Model
Freundlich Model
Effect of Initial
Conclusions

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