2013
DOI: 10.1007/s00289-012-0898-4
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Removal of methylene blue from aqueous solution by sorption on lignocellulose-g-poly(acrylic acid)/montmorillonite three-dimensional cross-linked polymeric network hydrogels

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Cited by 73 publications
(27 citation statements)
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“…It was calculated that the maximum adsorption capacity of hydrogel towards MB is 434.8 mg g −1 , comparable with those of graphene oxide-chitosan hydrogels (390 mg g −1 ) [28] and graphene oxide sponge (387 mg g −1 ) [29] , and much larger than those of chitosan beads (99 mg g −1 ) [30] , C 2 -symmetric benzene-based hydrogels (53.38 mg g −1 ) [31] and swede rape straw (246.4 mg g −1 ) [32] . Although most of polymer adsorbents, such as sodium humate/polyacrylamide/clay hybrid hydrogels (800 mg g −1 ) [33] , lignocellulose- g -poly(acrylic acid)/montmorillonite hydrogels (1994.38 mg g −1 ) [34] and poly(2-acrylamido-2-methylpropane sulfonic acid-co-itaconic acid) hydrogels (1000 mg g −1 ) [35] , exhibit quite high adsorption capacities, they can not be regenerated and do not satisfy environmental requirements. Designing and synthesizing new types of hydrogel with efficient adsorption and regenerative properties is an essential subject in the removal of dyes from wastewater.…”
Section: Resultsmentioning
confidence: 99%
See 1 more Smart Citation
“…It was calculated that the maximum adsorption capacity of hydrogel towards MB is 434.8 mg g −1 , comparable with those of graphene oxide-chitosan hydrogels (390 mg g −1 ) [28] and graphene oxide sponge (387 mg g −1 ) [29] , and much larger than those of chitosan beads (99 mg g −1 ) [30] , C 2 -symmetric benzene-based hydrogels (53.38 mg g −1 ) [31] and swede rape straw (246.4 mg g −1 ) [32] . Although most of polymer adsorbents, such as sodium humate/polyacrylamide/clay hybrid hydrogels (800 mg g −1 ) [33] , lignocellulose- g -poly(acrylic acid)/montmorillonite hydrogels (1994.38 mg g −1 ) [34] and poly(2-acrylamido-2-methylpropane sulfonic acid-co-itaconic acid) hydrogels (1000 mg g −1 ) [35] , exhibit quite high adsorption capacities, they can not be regenerated and do not satisfy environmental requirements. Designing and synthesizing new types of hydrogel with efficient adsorption and regenerative properties is an essential subject in the removal of dyes from wastewater.…”
Section: Resultsmentioning
confidence: 99%
“…As a continuous work, herein clay nanocomposite hydrogels were further functionalized and applied for adsorption of organic dyes such as methylene blue (MB), and heavy metal ions, the removal of which has drawn increasing attention in recent years due to their long-term environmental toxicity and short-term public health damage. Here, a self-standing membrane, produced from tough and elastic hydrogel, was used for the adsorption study, instead of shapes from other groups, where fragile hydrogel particles or dried gel powders are commonly employed [13] [15] . 2-acrylamide-2-methylpropanesulfonic acid sodium salt (AMPSNa) was chosen as a modifier and added into the hydrogel network to improve adsorption efficiency, since –SO 3 H groups in the AMPSNa have a high affinity towards dye molecules and heavy metal ions.…”
Section: Introductionmentioning
confidence: 99%
“…To interpret the adsorption system nature, several kinetic models were used to construe the experimental data that accessed from adsorption experiments. Kinetic isotherms were analysed according to Pseudo-firstand second-order kinetic models [43]. The equation of Pseudo-first-order is formulated as follows [44]:…”
Section: 2e Kinetic Studiesmentioning
confidence: 99%
“…Besides increasing the number of hydrophilic groups, increasing adsorption sites of hydrogel is also helpful to enhance the adsorption property. Incorporating clay into hydrogel to prepare composite hydrogel is an efficient method to increase the adsorption sites [12][13][14][15]. Montmorillonite [6,16], laponite [17], vermiculite [14], sepiolite [15], and attapulgite [18] have been used to prepare composites hydrogels.…”
Section: Introductionmentioning
confidence: 99%