| Literature DB >> 23493059 |
Siti Farhana Abdul Raof1, Sharifah Mohamad, Mhd Radzi Abas.
Abstract
A molecularly imprinted silica gel sorbent for selective removal of 2-Hydroxybenzoic acid (2-HA) was prepared by a surface imprinting technique with a sol-gel process. The 2-HA molecularly imprinted silica gel (2-HA-MISG) sorbent was evaluated by various parameters, including the influence of pH, static, kinetic adsorption and selectivity experiments. The optimum adsorption capacity to the 2-HA appeared to be around pH 2 by the polymer. Morevoer, the imprinted sorbent displayed fast uptake kinetics, obtained within 20 min. The adsorption capacity of the 2-HA-MISG (76.2 mg g-1) was higher than that of the non-imprinted silica gel (NISG) (42.58 mg g-1). This indicates that the 2-HA-MISG offers a higher affinity for 2-HA than the NISG. The polymer displays good selectivity and exhibits good reusability. Experimental results show the potential of molecularly imprinted silica sorbent for selective removal of 2-HA.Entities:
Year: 2013 PMID: 23493059 PMCID: PMC3634457 DOI: 10.3390/ijms14035952
Source DB: PubMed Journal: Int J Mol Sci ISSN: 1422-0067 Impact factor: 5.923
Figure 1Schematic mechanism of 2-HA-MISG preparation.
Figure 2SEM micrographs of (a) 2-HA-MISG (×500 magnification) and (b) NISG (×500 magnification).
Porosities of particles determined by the BET analysis.
| Sample | 2-HA-MISG | NISG |
|---|---|---|
| BET surface area (m2g−1) | 123.4 | 102.2 |
| Pore volume (m3g−1) | 0.4067 | 0.2873 |
| Pore size (nm) | 131.9 | 112.5 |
Figure 3IR spectra of activated silica gel (a), 2-HA-imprinted (b) and non-imprinted sorbents (c).
Figure 4Effect of pH on 2-HA adsorption.
Figure 5Effect of time on 2-HA adsorption.
Figure 6Effect of concentration on 2-HA adsorption.
Figure 7Selectivity study on 2-HA, 3-HA, 4-HA, and phenol.
Competitive loading of 2-HA, 4-HA, 3-HA and phenol by the imprinted and non-imprinted sorbents.
| Sorbents | Imprinted | Non-imprinted | |
|---|---|---|---|
| K | 2-HA | 4.257 | 0.485 |
| 4-HA | 0.3193 | 0.1207 | |
| 3-HA | 0.2918 | 0.277 | |
| phenol | 1.05 | 0.2013 | |
| α | 4-HA | 13.33 | 4.018 |
| 3-HA | 14.59 | 1.751 | |
| phenol | 4.054 | 2.409 | |
| IF | 4-HA | 3.318 | - |
| 3-HA | 8.3332 | - | |
| phenol | 1.683 | - |
distribution coefficient, K = {(Ci − Cf)/Cf} × {volume of solution (mL)}/{mass of sorbent (g)}, where Ci and Cf represent the initial and final concentrations, respectively; selectivity coefficient, α = K(2-HA)/K(4-HA or 3-HA or phenol); imprinting factor, IF = IFimprinted/IFnon-imprinted; Initial concentration, Ci = 10 ppm;
results based on three replicate analyses for all analytes.
Extraction recyclability through five extraction/stripping cycle.
| Extraction cycle | Loading capacity (mg/g) | Uptake (%) |
|---|---|---|
| 1 | 4.123 | 82.88 |
| 2 | 4.317 | 86.34 |
| 3 | 4.335 | 87.13 |
| 4 | 4.298 | 86.39 |
| 5 | 4.354 | 87.07 |
Method validation of 2-HA in real samples at different spiking levels.
| Samples | Spike (ppm) | Recovery (%) | RSD (%) |
|---|---|---|---|
|
| |||
| 1 | 0.2 | 86.89 | 0.36 |
| 1 | 93.02 | 0.61 | |
| 2 | 0.2 | 98.27 | 0.05 |
| 1 | 101.9 | 0.18 | |
| 3 | 0.2 | 105 | 0.23 |
| 1 | 96.2 | 0.97 | |
| 4 | 0.2 | 91.2 | 1.60 |
| 1 | 96.92 | 1.66 | |