Abstract

The recovery of La(III) and Ni(II) ions by a macroporous cation exchanger in sodium form (Lewatit Monoplus SP112) has been studied in batch experiments under varying HNO3 concentrations (0.2–2.0 mol/dm3), La(III) and Ni(II) concentrations (25–200 mg/dm3), phase contact time (1–360 min), temperature (293–333 K), and resin mass (0.1–0.5 g). The experimental data revealed that the sorption process was dependent on all parameters used. The maximum sorption capacities were found at CHNO3 = 0.2 mol/dm3, m = 0.1 g, and T = 333 K. The kinetic data indicate that the sorption followed the pseudo-second order and film diffusion models. The sorption equilibrium time was reached at approximately 30 and 60 min for La(III) and Ni(II) ions, respectively. The equilibrium isotherm data were best fitted with the Langmuir model. The maximum monolayer capacities of Lewatit Monoplus SP112 were equal to 95.34 and 60.81 mg/g for La(III) and Ni(II) ions, respectively. The thermodynamic parameters showed that the sorption process was endothermic and spontaneous. Moreover, dynamic experiments were performed using the columns set. The resin regeneration was made using HCl and HNO3 solutions, and the desorption results exhibited effective regeneration. The ATR/FT-IR and XPS spectroscopy results indicated that the La(III) and Ni(II) ions were coordinated with the sulfonate groups.

Highlights

  • Nowadays the world is dependent on natural resources mined from the earth, but they may run out

  • This indicate that the intraparticle diffusion process does not play a main role in the process rate controlling. These results show that the film diffusion is involved mainly in the La(III) and Ni(II) ions sorption onto Lewatit Monoplus SP112

  • This paper investigated the sorption process of La(III) and Ni(II) ions on Lewatit Monoplus SP112 by conducting batch and column experiments under different conditions

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Summary

Introduction

Nowadays the world is dependent on natural resources mined from the earth, but they may run out. There are millions of old and disused electronic and electrical devices around the world, so-called Waste Electrical & Electronic Equipment (WEEE) at our homes, i.e., old cell phones, smartphones, laptops, computers, non-working printers, and many others. WEEE is becoming the fastest growing waste stream in the world [1,2,3]. In 2016 the total e-waste was 44.7 Mt worldwide, and it is expected to grow to 52.2 Mt in 2021 [4]. Each of these devices contains a wide range of valuable metals as well as hazardous substances. Improper WEEE waste management can cause serious health and environmental problems as well as loss of many precious metals

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