Abstract

Electrodialysis (ED) was first established for water desalination and is still highly recommended in this field for its high water recovery, long lifetime and acceptable electricity consumption. Today, thanks to technological progress in ED processes and the emergence of new ion-exchange membranes (IEMs), ED has been extended to many other applications in the food industry. This expansion of uses has also generated several problems such as IEMs’ lifetime limitation due to different ageing phenomena (because of organic and/or mineral compounds). The current commercial IEMs show excellent performance in ED processes; however, organic foulants such as proteins, surfactants, polyphenols or other natural organic matters can adhere on their surface (especially when using anion-exchange membranes: AEMs) forming a colloid layer or can infiltrate the membrane matrix, which leads to the increase in electrical resistance, resulting in higher energy consumption, lower water recovery, loss of membrane permselectivity and current efficiency as well as lifetime limitation. If these aspects are not sufficiently controlled and mastered, the use and the efficiency of ED processes will be limited since, it will no longer be competitive or profitable compared to other separation methods. In this work we reviewed a significant amount of recent scientific publications, research and reviews studying the phenomena of IEM fouling during the ED process in food industry with a special focus on the last decade. We first classified the different types of fouling according to the most commonly used classifications. Then, the fouling effects, the characterization methods and techniques as well as the different fouling mechanisms and interactions as well as their influence on IEM matrix and fixed groups were presented, analyzed, discussed and illustrated.

Highlights

  • Licensee MDPI, Basel, Switzerland.Electrodialysis (ED) was first established for water treatment applications, principal-ly for water desalination [1,2,3,4] and is still highly used and recommended in this field for its high water recovery, long lifetime compared to other usual technologies and acceptable electricity consumption [5]

  • The nitrogen content observed for the cation exchange membrane (CEM) pretreated in HCl solution after soaking in the soy protein hydrolysate solution (SPHS) would be 12% higher than the ones pretreated by distilled water and

  • The results showed the intensification of C=C stretching bands of polyphenol aromatic rings in both membranes but this was more intense in CEMs

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Summary

Introduction

Age-ing mechanisms cleaningand operations, etc.) [16,17,18] These aspects are not(prolonged sufficientlyuse, controlled mastered,fouling the usephenomena, and the efficiency of ED. We focused issues interest of IEM fouling in the industry used and it should be noted that this is a subjecton ofthe common to all types of ED membranes it should be noted that this is a subject of common interest to all types of membranes used in all baromembrane [2,19,20] and electromembrane [21,22,23,24] methods. 1 presents evolution of the number of publications on the topic of fouling and scaling of IEMs comthe evolution of the number of publications on the topic of fouling and scaling of IEMs paring to other industrial filtration membranes fromfrom to 2020.

Evolution
Methods of Theirterm
Mineral Foulants
SEM images and processing
Photographs ofED
Organic Foulants and Colloidal Particles
11. Synchrotron Fourier
Biofouling
Localization of Foulants and Surface Roughness Parameters
Another
AMX-Sbw723
Mechanisms
Physicochemical Interactions
26. The byby thethe ion-exchange resins vs time of itofsoaking in the
Stretching of the Polymer ion Exchange Matrix
POregularly
Findings
Conclusions
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