Application of Chitosan for the Removal of Metals From Wastewaters by Adsorption—Mechanisms and Models Review
By C. Gérente, V. Lee, P. Cloirec, Gordon McKay. 2007
765 citations recorded by the source corpus.
Subfields: Biomaterials, Water Science and Technology
View Paper: https://www.semanticscholar.org/paper/1e2d9bdf00f9185e24d91402283b9a3625d1ef40
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In Biomaterials
In Water Science and Technology
Citations in the corpus
- Removal of heavy metals from aqueous solution by biochars derived from anaerobically digested biomass. (2012, background): “These governing equations can be written as (Cao et al., 2009; Gerente et al., 2007):”
- Study of the adsorption of Cd (II) from aqueous solution using zeolite-based geopolymer, synthesized from coal fly ash; kinetic, isotherm and thermodynamic studies (2015, methodology): “Elovich equation is given as [Gerente et al., 2007]: qt = 1/ β ln (α β) + 1/ β ln t (8) Where α (mmol.g-1.min-1) is the initial adsorption rate and β (g.mmol-1) is the desorption constant related to the extent of the surface coverage and activation energy for chemisorption.”
- Chitosan nanoparticles extracted from shrimp shells, application for removal of Fe(II) and Mn(II) from aqueous phases (2018, background): “Chitosan has the ability to adsorb significant amounts of metal ions over a wide range.([4,8]) Chitosan is a polysaccharide which is made from the chitin present in the exoskeletons of the various crustaceans.”
- Removal of arsenic, methylene blue, and phosphate by biochar/AlOOH nanocomposite (2013, methodology): “While the Elovich model is an empirical equation considering the contribution of desorption, the first-order and second-order models are semimechanistic models based on the mononuclear and binuclear adsorption mechanisms, respectively [29].”
- Remediation of Heavy Metals by Biomolecules: A Review (2015, methodology): “The Redlich-Peterson model gathers the features of the Langmuir and Freundlich isotherms in a single equation (Febrianto et al., 2009; Gerente et al., 2007).”
- Synthesis, characterization, and dye sorption ability of carbon nanotube–biochar nanocomposites (2014, methodology): “The pseudo-second order model, which predominantly describes chemisorption processes and interaction of functional groups on sorbents with contaminants [42], was the best fit for BC–CNT-1% sorption kinetics data (R(2) = 0.”
- Characterization and environmental applications of clay–biochar composites (2014, neutral): “where K, Kf, Klf, and Kr represents the four models’ coefficient, respectively; Q (mg g ) denotes the maximum capacity; Ce (mg L ) is the sorbate concentration at equilibrium; and n and a are constants for Freundlich and Redlich–Peterson models, respectively [49].”
- The past, present, and future trends of biosorption (2010, background): “[58] also summarized the biosorptive capacities of chitin/chitosan and its many derivatives.”