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. 2022 Jul 7;12(31):19741-19750.
doi: 10.1039/d2ra02980d. eCollection 2022 Jul 6.

Ionic liquid-immobilized silica gel as a new sorbent for solid-phase extraction of heavy metal ions in water samples

Affiliations

Ionic liquid-immobilized silica gel as a new sorbent for solid-phase extraction of heavy metal ions in water samples

The Thai Nguyen et al. RSC Adv. .

Abstract

In the current study, we have developed a solid-phase extraction (SPE) method with novel C18-alkylimidazolium ionic liquid immobilized silica (SiO2-(CH2)3-Im-C18) for the preconcentration of trace heavy metals from aqueous samples as a prior step to their determination by inductively coupled plasma mass spectrometry (ICPMS). The material was characterized by Fourier-transform Infrared Spectroscopy (FTIR), Scanning Electron Microscopy (SEM), Thermogravimetric Analysis (TGA), Energy-Dispersive X-ray Spectroscopy (EDS), and Brunauer-Emmett-Teller (BET) analysis. A mini-column packed with SiO2-(CH2)3-Im-C18 sorbent was used for the extraction of the metal ions complexed with 1-(2-pyridylazo)-2-naphthol (PAN) from the water sample. The effects of pH, PAN concentration, length of the alkyl chain of the ionic liquid, eluent concentration, eluent volume, and breakthrough volume have been investigated. The SiO2-(CH2)3-Im-C18 allows the isolation and preconcentration of the heavy metal ions with enrichment factors of 150, 60, 80, 80, and 150 for Cr3+, Ni2+, Cu2+, Cd2+, and Pb2+, respectively. The limits of detection (LODs) for Cr3+, Ni2+, Cu2+, Cd2+, and Pb2+ were 0.724, 11.329, 4.571, 0.112, and 0.819 μg L-1, respectively with the relative standard deviation (RSD) in the range of 0.941-1.351%.

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Conflict of interest statement

The authors have no conflicts to declare.

Figures

Scheme 1
Scheme 1. Synthetic procedure of SiO2–(CH2)3–Im–C18.
Fig. 1
Fig. 1. FT-IR spectra of (a) SiO2 (1), (b) SiO2–(CH2)3–Cl (2), (c) SiO2–(CH2)3–Im (4), (d) SiO2–(CH2)3–Im–C18 (5).
Fig. 2
Fig. 2. Thermal gravimetric analysis diagram of SiO2–(CH2)3–Im–C18.
Fig. 3
Fig. 3. Energy-dispersive X-ray spectroscopy of SiO2–(CH2)3–Im–C18.
Fig. 4
Fig. 4. SEM image of SiO2–(CH2)3–Im–C18.
Fig. 5
Fig. 5. BET of SiO2–(CH2)3–Im–C18.
Fig. 6
Fig. 6. Effect of pH on the sorption percentage. Utilized conditions: Cr3+, Ni2+, Cu2+, Cd2+, and Pb2+ 50 μg L; volume: 50 mL; PAN: 2 × 10−5 mol.L−1; flow rate: 0.8 mL.min−1.
Fig. 7
Fig. 7. Effect of PAN concentration on SiO2–(CH2)3–Im–C18. Utilized conditions: Cr3+, Ni2+, Cu2+, Cd2+, and Pb2+ 50 μg L; volume: 50 mL; flow rate: 0.8 mL.min−1.
Fig. 8
Fig. 8. Effect of the length of alkyl chain.
Fig. 9
Fig. 9. Effect of nitric acid concentration on the elution recovery.
Fig. 10
Fig. 10. Effect of sample volume on sorption percent.
Fig. 11
Fig. 11. Determination of Cr3+, Ni2+, Cu2+, Cd2+, and Pb2+ in water samples. Average of three determinations ± standard deviation (SD), n = 3.

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