2021
DOI: 10.1016/j.eti.2020.101244
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Kinetic studies validated by Artificial Neural Network simulation for the removal of dye from simulated waste water by the activated carbon produced from Acalypha indica leaves

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Cited by 9 publications
(4 citation statements)
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“…In this regard, the impact of contact time on the removal of MO dye by activated carbon is depicted in Figure 6(d). From the results, it is inferred the equilibrium time and CT are in a direct relationship, i.e., adsorption increases with increase in time and attains equilibrium at the maximum adsorption capacity of adsorbent, which is attributed to the availability of adequate surface active sites on the sorbent surface for the adsorption of dye [38]. However, after reaching 180 min of CT, the equilibrium state has been reached due to the reduction of available active sites followed by the lowered concentration gradient of MO dye.…”
Section: Resultsmentioning
confidence: 92%
See 1 more Smart Citation
“…In this regard, the impact of contact time on the removal of MO dye by activated carbon is depicted in Figure 6(d). From the results, it is inferred the equilibrium time and CT are in a direct relationship, i.e., adsorption increases with increase in time and attains equilibrium at the maximum adsorption capacity of adsorbent, which is attributed to the availability of adequate surface active sites on the sorbent surface for the adsorption of dye [38]. However, after reaching 180 min of CT, the equilibrium state has been reached due to the reduction of available active sites followed by the lowered concentration gradient of MO dye.…”
Section: Resultsmentioning
confidence: 92%
“…The sorbent dosage is varied from 0.8 to 2 g and the q m value of adsorbent is raised from 0.829 to 1.357 mg g −1 , respectively. Improved dye penetration is facilitated by the available large surface area of sorbent and accessibility of adsorption sites [38]. At q m = 1.2 g, the maximum uptake capacity reaches an equilibrium state.…”
Section: Resultsmentioning
confidence: 99%
“…Other recent studies on the ANN modeling of adsorption isotherms and kinetics include the fluoride adsorption on rice husk-derived biochar modified with Fe or Zn [158], the removal of brilliant green dye using mesoporous Pd–Fe magnetic nanoparticles immobilized on reduced graphene oxide [15], the adsorption of diazinon pesticide on a magnetic composite clay/graphene oxide/Fe 3 O 4 [159], the removal of crystal violet and methylene blue on magnetic iron oxide nanoparticles loaded with cocoa pod carbon composite [160], the arsenide removal employing mesoporous CoFe 2 O 4 /graphene oxide nanocomposites [161], the adsorption of perfluorooctanoic acid on copper nanoparticles and fluorine-modified graphene aerogel [17], the uptake of dicamba (3,6-dichloro-2-methoxy benzoic acid) by MIL-101(Cr) metal-organic framework [16], the phosphorous adsorption on polyaluminum chloride water treatment residuals [162], the use of iron doped-rice husk for the chromium adsorption/reduction [163], the removal of methyl orange dye by an activated carbon derived from Acalypha indica leaves [164], the lead adsorption by a hydrochar obtained from the KOH activated Crocus sativus petals [165], the adsorption of the cefixime antibiotic using magnetic composite beads of reduced graphene oxide-chitosan [13], the use of graphene oxide-cyanuric acid nanocomposite for the lead adsorption [14], the arsenic removal by an adsorbent consisting of iron oxide incorporated carbonaceous nanomaterial derived from waste molasses [12], the fluoride adsorption by chemically activated carbon prepared from industrial paper waste [18], the methylene blue adsorption with polyvinyl alcohol/carboxymethyl cellulose-based hydrogels [166], the modeling of adsorption properties of biochar and resin for the removal of organic compounds [167], and the removal of lead from waster with a magnetic nanocomposite [168].…”
Section: Applications Of Anns To Model the Adsorption Of Water Pollut...mentioning
confidence: 99%
“…It has the advantages of low cost, no secondary pollution, high efficiency, and eco-friendly recycling resources [ 9 ]. Currently, the desired bioremediation materials can be obtained from various sources, such as the plants Acalypha indica [ 10 ], Saccharomyces [ 11 ], Aspergillus [ 12 ], white-rot fungi [ 13 ], and algae [ 14 , 15 ], which have been widely used for the removal of organic pollutants from wastewater. In addition, it has been reported that peroxidases [ 16 ] and laccases [ 17 , 18 ] among biological enzymes also degrade organic pollutants; however, existing studies have shown that free microorganisms/enzymes have low stability, short service lives, and are not easy to separate and recover, which limits their further industrial application [ 19 ].…”
Section: Introductionmentioning
confidence: 99%