2018
DOI: 10.17576/jsm-2018-4706-12
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Synthesis, Characterization and Adsorption Study of C-4-Phenacyloxy-phenylcalix [4]resorcinarene for Pb(II), Cd(II) and Cr(III) Ions

Abstract: Jerapan C-4-fenasiloksifenilkaliks[4]resorsinarena terhadap Pb(II), Cd(II) dan Cr(III)) UNDRI RASTUTI, DWI SISWANTA, WISNU PAMBUDI, BETA ACHROMI NUROHMAH, BOHARI M. YAMIN & JUMINA* ABSTRACT C-4-phenacyloxy phenyl calix[4]resorcinarene (CPPCR) was synthesized by acidic condensation of 4-hydroxybenzaldehyde and resorcinol. The adsorption of CPPCR for Pb(II), Cd(II) and Cr(III) has been studied by measuring the metal concentration in aqueous solution using Atomic Absorption Spectrophotometry (AAS). The effects of… Show more

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Cited by 5 publications
(5 citation statements)
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“…The pseudo-1 st order model has also been reported to be the best model for cadmium sorption onto nano-clay/TiO2 composite [25], coco-peat biomass [26], alginate-calcium carbonate composite beads [27], poly(acrylamide-co-sodium methacrylate) hydrogels [28], the bacterium, Salmonella enterica 43C [29], water hyacinth (Eichhornia crassipes) biochar alginate beads [30], zerovalent iron nanoparticles [31] and Mactra aequisulcata shells [32]. On the other hand, the pseudo-2 nd order kinetics model has been reported to be the best model in several other cadmium sorption studies such as sorption of cadmium onto C-4-phenacyloxy-phenylcalix [4], resorcinarene [33], modified palm shell powder [34], chemically modified biomass from Triticum aestivum [35] and several other heavy metals such as the biosorption of Cr(VI) to magnetic iron oxide nanoparticlemulti-walled carbon nanotube [36], Cu(II) adsorption onto functionalized cellulose beads from Tunisian almond (Prunus dulcis) shell [37], the sorption of Zn(II) by Streptomyces ciscaucasicus [38] and other heavy metals [23,[39][40][41][42][43].…”
Section: Discussionmentioning
confidence: 99%
“…The pseudo-1 st order model has also been reported to be the best model for cadmium sorption onto nano-clay/TiO2 composite [25], coco-peat biomass [26], alginate-calcium carbonate composite beads [27], poly(acrylamide-co-sodium methacrylate) hydrogels [28], the bacterium, Salmonella enterica 43C [29], water hyacinth (Eichhornia crassipes) biochar alginate beads [30], zerovalent iron nanoparticles [31] and Mactra aequisulcata shells [32]. On the other hand, the pseudo-2 nd order kinetics model has been reported to be the best model in several other cadmium sorption studies such as sorption of cadmium onto C-4-phenacyloxy-phenylcalix [4], resorcinarene [33], modified palm shell powder [34], chemically modified biomass from Triticum aestivum [35] and several other heavy metals such as the biosorption of Cr(VI) to magnetic iron oxide nanoparticlemulti-walled carbon nanotube [36], Cu(II) adsorption onto functionalized cellulose beads from Tunisian almond (Prunus dulcis) shell [37], the sorption of Zn(II) by Streptomyces ciscaucasicus [38] and other heavy metals [23,[39][40][41][42][43].…”
Section: Discussionmentioning
confidence: 99%
“…Obviously point of zero charge (pHpzc) is an imperative parameter to determine the net density of surface charge of biosorbent in solution [39] . According to the study of Rastuti et al [40] the pHpzc was calculated from the plot of ΔpH Vs. pHinitial, the intersection points at which ∆pH = 0 specify by the value of pHpzc as shown in Figure 6. The point of zero charge was the pH at which the modified cellulose net surface charge was zero, the surface of the modified cellulose has a negative charge when pH > pHpzc and a positive charge at pH < pHpzc.…”
Section: Analysis Of Phpzcmentioning
confidence: 99%
“…On the other hand, the pseudo-2 nd order kinetics model has been reported to be the best model in several lead sorption studies such as lead(II) sorption by Cephalosporium aphidicola [31], on sesame leaf [32] and on Spirodela polyrhiza [33] to name a few. In general, the pseudo-2 nd order was the best model for metal sorption such as the biosorption of Cr(VI) to magnetic iron oxide nanoparticlemulti-walled carbon nanotube [34], Cu(II) adsorption onto functionalized cellulose beads from Tunisian almond (Prunus dulcis) shell [35] and the sorption of Zn(II) by Streptomyces ciscaucasicus [36] and other heavy metals [20,24,[37][38][39][40][41][42][43], indicating that the pseudo-2 nd model is routinely reported to be better than the pseudo-1 st order in fitting kinetics of xenobiotics sorption although this discrepancy has been attributed to the mathematically versatile properties of the pseudo-2 nd order model [2,16,44].…”
Section: The Best Kinetic Model For Adsorption Of Lead (Ii) Wasmentioning
confidence: 99%