Treatment Methods for Lead Removal from Wastewater

Ahmad, Iftikhar; Asad, Umair; Maryam, Laraib; Masood, Marriam; Saeed, Muhammad Farhan; Jamal, Aftab; Mubeen, Muhammad

doi:10.1007/978-3-031-37327-5_10

Cited by 4 publications

(1 citation statement)

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“…The maximum permissible limit of Pb(II) in drinking water by WHO is 0.05 mg/L [ 9 ]. Effective methods for lead removal include chemical precipitation, membrane filtration, reverse osmosis, ion exchange, biosorption, and adsorption [ 6 , 14 ].…”

Section: Introductionmentioning

confidence: 99%

Equilibrium, Kinetic, and Diffusion Mechanism of lead(II) and cadmium(II) Adsorption onto Commercial Activated Carbons

Lach,

Okoniewska

2024

Molecules

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The adsorption of Pb(II) and Cd(II) on three commercial microporous activated carbons was analysed. Adsorption kinetics and statistics were investigated, and the results were described with different models. The highest values of the correlation coefficient R2 were obtained for the pseudo-second-order kinetics model for all ions tested and all sorbents used. The adsorption process was found to be determined by both diffusion in the liquid layer and intraparticle diffusion. The adsorption equilibrium is very well described by Langmuir, Temkin, Thoth or Jovanovic isotherm models. Based on the values of n from the Freundlich isotherm and KL from the Langmuir isotherm, the adsorption of cadmium and lead ions was found to be favourable. The highest monolayer capacities were obtained during the adsorption of lead ions (162.19 mg/g) and for cadmium (126.34 mg/g) for activated carbon WG-12. This carbon is characterised by the highest amount of acid functional groups and the largest specific surface area. The adsorption efficiency of the tested ions from natural water is lower than that from a model solution made from deionised water. The lowest efficiencies are obtained when the process occurs from highly mineralised water.

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Section: Introductionmentioning

confidence: 99%