2003
DOI: 10.1016/s0960-8524(03)00129-9
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Cocoa shells for heavy metal removal from acidic solutions

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Cited by 223 publications
(89 citation statements)
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“…The sorption capacity of Indian WBAP for chromium (III) at pH 2.36 and 295 K was found to be 12.07 mg/g. The sorption capacity obtained for WBAP was found to be comparable to and in some cases better than the other sorbents and activated carbons as reported by Hasany and Ahmad (2006) for coconut husk (0.949 mg/g); Gode and Phelivan (2007) for b-DAEGsporopollenin resin (1.23 mg/gm) and CEPsporopollenin resin (133.33 mg/gm); Han et al (2006) for chlorella miniata (14.73 mg/g); Natale et al (2006) for char of South African coal (0.285 mg/g) and granular activated carbon (2.21 mg/g); Entezari et al (2005) for tire rubber (0.85 mg/g); Meunier et al (2003) for cocoa schells (2.52 mg/g); Bessiere et al (2002) for bentonite (4.29 mg/g) and perlite (1.4 mg/g) and Abollino et al (2002) for Na-montmorillonite (5.13 mg/g). The numerical value of mean sorption energy (E) from DKR isotherm in the present system was found to be 12.909 kJ/mol indicating the sorption process to be of ion exchange in nature.…”
Section: Modeling Of the Sorption Isothermsmentioning
confidence: 99%
“…The sorption capacity of Indian WBAP for chromium (III) at pH 2.36 and 295 K was found to be 12.07 mg/g. The sorption capacity obtained for WBAP was found to be comparable to and in some cases better than the other sorbents and activated carbons as reported by Hasany and Ahmad (2006) for coconut husk (0.949 mg/g); Gode and Phelivan (2007) for b-DAEGsporopollenin resin (1.23 mg/gm) and CEPsporopollenin resin (133.33 mg/gm); Han et al (2006) for chlorella miniata (14.73 mg/g); Natale et al (2006) for char of South African coal (0.285 mg/g) and granular activated carbon (2.21 mg/g); Entezari et al (2005) for tire rubber (0.85 mg/g); Meunier et al (2003) for cocoa schells (2.52 mg/g); Bessiere et al (2002) for bentonite (4.29 mg/g) and perlite (1.4 mg/g) and Abollino et al (2002) for Na-montmorillonite (5.13 mg/g). The numerical value of mean sorption energy (E) from DKR isotherm in the present system was found to be 12.909 kJ/mol indicating the sorption process to be of ion exchange in nature.…”
Section: Modeling Of the Sorption Isothermsmentioning
confidence: 99%
“…These include mungbean husk [5], hazelnut shell [6], almond shell [6], pine [7], lignin [8], tea leaves [9], tree ferm [10], groundnut husks [11], sphagnum moss peat [12], sawdust [13], rice hulls [14], chitosan [14], sugarcane bagasse [15], cocoa shell [16], and rice husk [17]. However, some major limitations of these biosorptions are that some of them have not yielded satisfactory results (high metal adsorption capacity) and others that yielded good results may not locally be available.…”
Section: Introductionmentioning
confidence: 99%
“…It is used in mining, smelting, refining, battery manufacturing, soldering, electrical wiring, home demolition and construction, painting, ceramic glazing, and the making of stained glass. The increasing presence of lead is very problematic to surface water and underground water due to their mobility and great toxicity (Meunier et al, 2003;Yan and Viraraghavan, 2003). The heavy metal lead is among the most common pollutant found in industrial effluents.…”
mentioning
confidence: 99%