| Literature DB >> 33553728 |
Gabriella Josephine Maranata1, Natasha Octavianti Surya1, Aliya Nur Hasanah1,2.
Abstract
Molecular imprinted solid-phase extraction is the technique that uses molecular imprinted polymer as the sorbent in solid phase extraction. Molecular imprinted solid-phase extraction is effective and efficient for the extraction process and cleaning as compared with solid phase extraction (SPE) without molecular imprinted polymer. The complexity of variables in molecular imprinted solid-phase extraction arise as problems in the analysis, therefore it is necessary to optimize the extraction conditions of molecular imprinted solid-phase extraction. To achieve the sorption equilibrium and achieve the shortest time, certain parameters such as contact time, ion strength of sample, pH of sample, amount of sorbent, sample flow rate, addition of salt and buffer solution, washing solvent, elution solvent, and loading solvent need to be optimized. The selection of suitable properties and quantities of each factor greatly affect the formation of appropriate interactions between the sorbent and analytes. Percentage recovery is also influenced by formation of the appropriate bonds, sample flow rates, extraction time, salt addition, and sorbent mass. Therefore, in the future, molecular imprinted solid-phase extraction optimization has to consider and adjust various factors reviewed in this paper to form appropriate interactions between the absorbent and target molecules which have an impact on the optimal results.Entities:
Keywords: Molecular imprinted solid phase extraction; Sorption equilibrium; Variables in MISPE
Year: 2021 PMID: 33553728 PMCID: PMC7848654 DOI: 10.1016/j.heliyon.2021.e05934
Source DB: PubMed Journal: Heliyon ISSN: 2405-8440
Figure 1Molecular imprinted solid phase extraction (MISPE) procedure.
Figure 2Steps in offline modes.
Figure 3Steps in online mode.
Advantages and disadvantages of offline and online modes.
| Mode of MISPE | Advantage | Disadvantage |
|---|---|---|
| Offline Mode | Overall operation has a lot of choices of solvents and additives [ | The disadvantages of offline mode is contamination of analytes and potential loss (It caused by the sample handling requirements include isolation, preconcentration and injection into instrument) [ |
| The operation quite simple and easy. Hence, enrichment rate and selectivity in this mode are higher [ | This mode takes a long time for operation, so the error will be increased and use several organic solvents in washing [ | |
| Online Mode | Directly connected with the chromatographic system [ | The disadvantages of this technique are the high pressure of the online system when the column is filled up with nano-sized materials and the addition of an SPE column that is easily damaged. A strategy has been proposed to control the drawbacks of column-based SPE by performing bead injection [ |
| Analysis time and analyte loss will be reduced by using online mode as well as sensitivity, accuracy, and precision will be increased by eliminating personal errors [ | ||
| The required amount of solvent is also lower and online mode allows partial or total automation of analytical steps [ | ||
| In this mode, the enrichment steps and sample cleaning are automated cause it can allow the direct injection of untreated samples. So the online mode has better limits of detection and reproducibility as compared to the offline mode [ |
Application of molecular imprinted solid phase extraction.
| Template | Sample | Target Analyte | Mode | Reference |
|---|---|---|---|---|
| 4,4′Methylenebisphenol | River organic matter | Bisphenol A | Off-line | [ |
| β-Agonists | Calf urine | β-Agonists | Off-line | [ |
| Bisphenol A | Spiked tap water and lake water | Bisphenol A | On-line | [ |
| Brombuterol | Human and calf urine | Clenbuterol | Off-line | [ |
| Bromoclenbuterol | Liver samples | Clenbuterol | Off-line | [ |
| Caffeine | Aqueous test samples, natural water, and human urine | Methylxanthines | Off-line | [ |
| Catechol | Effluent river water | Catechol | Off-line | [ |
| Cephalexin | Human serum | Cephalexin | On-line | [ |
| Cyanide | Waste water | Cyanide | Off-line | [ |
| Cotinine | Human urine | Cotinine | Off-line | [ |
| Dopamine hydrochloride | Urine | Adrenergic drugs | Off-line | [ |
| Ibuprofen | River water | Anti-inflammatory drugs | Off-line | [ |
| Monosulfuron | Soil samples | Monosulfuron | Off-line | [ |
| Monocrotophos | Water and soil | Organophophorus | Off-line | [ |
| Naproxen | Urine samples | Naproxen | Off-line | [ |
| Organotin | Environmental samples | Organotin | Off-line | [ |
| p-tert-butyl-phenol | Environmental water, purified water | Bisphenol A | On-line | [ |
| Pentachloro-phenol | Lake water, river water, and waste water | Pentachlorophenol | On-line | [ |
| Phenytoin | Plasma | Phenytoin | Off-line | [ |
| Pirimicarb | Tap water, spring water, river water, and sea water | Pirimicarb | On-line | [ |
| Propazine | River water | Triazines and their metabolites | Off-line | [ |
| Quercetin | Plasma | Quercetin | Off-line | [ |
| Terbuthylazine | River water | Triazines | On-line | [ |
| Verapamil | Urine and plasma and cell culture | Verapamil and gallopamil | On-line | [ |