THE SYNTHESIS OF ION-IMPRINTED POLYMERS FOR SEPARATION AND ANALYSIS OF CHROMIUM(III)

Chromium is widely used in metallurgy for the production of steel, ferrous and non- ferrous alloys, in industrial processes for electroplating, tanning, metal smelting, and in the chemical industry for the production of paints and pigments. As a result, large amounts of chromium compounds are releas...

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Bibliographic Details
Main Author: Kurniawati, Fitri
Format: Theses
Language:Indonesia
Subjects:
Online Access:https://digilib.itb.ac.id/gdl/view/57391
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Institution: Institut Teknologi Bandung
Language: Indonesia
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Summary:Chromium is widely used in metallurgy for the production of steel, ferrous and non- ferrous alloys, in industrial processes for electroplating, tanning, metal smelting, and in the chemical industry for the production of paints and pigments. As a result, large amounts of chromium compounds are released into the environment causing contamination of soil, surface water and groundwater. Chromium exists in the environment generally in two oxidation states, as compounds Cr(III) and Cr(VI), which have different physicochemical, toxicological and biological properties. Cr(III) is an important micronutrient that has an important role in glucose, lipid and protein metabolism, while Cr(VI) has a detrimental effect on living organisms. Exposure to Cr(VI) compounds to living organisms can cause damage to the skin, respiratory tract, kidneys and increase the risk of lung cancer. The purpose of this research is to make Ion Imprinted Polymers Cr(III)-IIP so that it can be used for selective separation of Cr(III) and Cr(VI) metal ions. The research stage begins with the formation of a metal-ligand complex between the metal ion Cr(III) and the diphenylcarbazone ligand. Furthermore, prepolymerization occurs between the metal-ligand complex and the functional monomer methacrylic acid. In the presence of ethylene glycol dimethacrylate as a crosslinker and benzoyl peroxide as an initiator, thermal polymerization occurs. The mole ratio of template ion, monomer and crosslinker used in this study was 0.4:4:20. Control polymers, namely NIP (Non-Imprinted Polymers) and NIP-DPCO (Non-Imprinted Polymers- Diphenylcarbazone) were synthesized by the same procedure but without the presence of template ions. The synthesized polymers of Cr(III)-IIP, NIP and NIP- DPCO were then characterized using FTIR (Fourier Transform Infra Red) and SEM (Scanning Electron Microscope). From the FTIR spectra of the three sorbents, there is a strong and wide peak at a wave number of 3489 cm-1 and a moderate peak at a wave number of 1633 cm-1 which indicates the presence of a COOH group on the polymer surface. Strong peaks at wave numbers 1732 cm-1 and 1163 cm-1 indicate stretching vibrations -C=O and -C-O vibrations of methacrylic acid. The FTIR spectra of NIP and NIP-DPCO were similar to the spectra of Cr(III)-IIP which indicated the similarity in the main chain structure of the polymer. The results of SEM characterization showed that bulk polymerization caused the morphology of Cr(III)-IIP to be irregular in shape and large in size. However, the surface morphology of NIP is much smoother, differing significantly from Cr(III)- IIP due to the absence of template ions in NIP synthesis. Optimization of Cr(III)- IIP was carried out by batch method and the optimum conditions for Cr(III)-IIP adsorption were obtained at pH 5 and a contact time of 30 minutes. The maximum adsorption capacity of Cr(III)-IIP, NIP and NIP-DPCO were 1.0880 mg g-1, 0.8998 mg g-1 and 0.3051 mg g-1, respectively. The IF value indicates the strength of the polymer interaction with the template ion. The IF Cr(III)-IIP/NIP-DPCO value is 3.57 (>1) while the IF Cr(III)-IIP/NIP value is 1.21 which indicates the interaction strength of the polymer to template ions is better when compared to NIP- DPCO rather than NIP. The pseudo-first order adsorption kinetics model can be used to describe the adsorption process very well. The adsorption process follows the Freundlich isotherm model which assumes that the adsorbate adsorbs onto the heterogeneous surface of the adsorbent and is layered. The selectivity test showed that Cr(III)-IIP was more selective towards Cr(III) metal ions than Cr(VI) metal ions. The adsorption-desorption test was carried out to see the recovery value where the % recovery obtained was 90.26%. From the analysis of river water samples, it can be seen that the accuracy of the developed method is quite good with a recovery value (% recovery) of 84.95%.