2019
DOI: 10.1246/bcsj.20190111
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Removal of Cationic or Anionic Dyes from Water Using Ion Exchange Cellulose Monoliths as Adsorbents

Abstract: This work deals with the preparation of poly(sodium p-styrenesulfonate) (PSS) and poly[(3-acryloylaminopropyl)trimethylammonium chloride] (APTAC) modified ion exchange cellulose monoliths (C-g-PSS and C-g-APTAC, respectively). The obtained ion exchange monoliths were employed for the removal of cationic or anionic dyes from aqueous solutions with particular reference to the effects of initial dye concentration, flow rate and ionic strength on adsorption. Detailed adsorption characteristics of ion exchange mono… Show more

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Cited by 39 publications
(9 citation statements)
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“…Various technologies involving chemical, physical, biochemical and combined treatment methods have been introduced and put in place to remove dye from textile wastewater. So far, co-precipitation, 17,18 coagulation, 19 solvent extraction, 20 otation, 21 electrochemical treatment, 22 ion exchange, 23 membrane ltration 24 and reverse osmosis 25 are among widely used dye removal technologies. Recently, Mesoporous Organo Silicate (PMOS) composites were synthesized and their photocatalytic degradation capacity for methylene blue was tested and an efficiency from 44 to 71% was achieved.…”
Section: Introductionmentioning
confidence: 99%
“…Various technologies involving chemical, physical, biochemical and combined treatment methods have been introduced and put in place to remove dye from textile wastewater. So far, co-precipitation, 17,18 coagulation, 19 solvent extraction, 20 otation, 21 electrochemical treatment, 22 ion exchange, 23 membrane ltration 24 and reverse osmosis 25 are among widely used dye removal technologies. Recently, Mesoporous Organo Silicate (PMOS) composites were synthesized and their photocatalytic degradation capacity for methylene blue was tested and an efficiency from 44 to 71% was achieved.…”
Section: Introductionmentioning
confidence: 99%
“…Currently, conventional technologies being adopted for the treatment of reactive dyes include photocatalytic degradation [ 7 ], enzymatic action [ 8 ], chemical coagulation/flocculation [ 9 ], ion exchange [ 10 ] and membrane separation [ 11 ], etc. At an industrial scale these conventional treatment processes have certain limitations: e.g., phase, shape, band gap, light source, structure, reactor design and catalyst recovery [ 12 ], the temperature specificity and alkaline conditions of laccase enzyme [ 13 ], residual sludge generation during chemical coagulation [ 14 ], slow pore diffusion, low accessible flow rates, high pressure drop and flow channeling in ion exchange [ 15 ], and chemical incompatibility in membrane separation [ 16 ], etc.…”
Section: Introductionmentioning
confidence: 99%
“…However, in most literatures the adsorption capacity of a column decreased with increasing flow rate [ 70 , 74 , 75 ]. Only a few authors reported increased column adsorption with increasing flowrate [ 76 , 77 , 78 ]. Column adsorption is based on complex phenomena such as axial dispersion, film diffusion resistance, intraparticle diffusion resistance (both pore and surface diffusion) and adsorption equilibrium with the adsorbent [ 79 , 80 ].…”
Section: Discussionmentioning
confidence: 99%