Review Article
Nanoparticles Used for Extraction of Polycyclic Aromatic Hydrocarbons
Table 4
Some PAHs extraction techniques.
| Sample matrix | Technique | Advantage | Limitation | Limit of detection | Recovery (%) | Ref |
| Retention pond water | SPE | Easy automation, analyzed many samples in parallel, requires no human intervention | Adsorption of PAHs on to the wall of extraction vessels, large solvent volume, involves many steps | 0.5–5 ng/L | 40–95 | [31] | Surface water | LLE | Extracts PAHs both dissolved in the water and adsorbed upon any suspended particles in the sample | Use of large volumes of solvents and numerous pieces of laboratory glassware, time-consuming, not easy to automate | 0.1–14 ng/L | 80–120 | [32] | Water | D-µ-SPE | Low cost, solvent minimization, materials used were more convenient in handling | Solvent type, significant effect of extraction and desorption time on the method performance | 0.013–0.73 ng/ml | 84–110 | [24] | Seawater | SPME | Solvent minimization, involved few steps, minimum sample volume, easy preparation | Limited capacity of the fiber, potential contamination of the SPME needle | 0.1–0.35 ng/g | 75.6–107 | [22] | Sea water | SBSE | Further sample preparation, e.g., by pH adjustment, back extraction, and derivatisation required for extraction of certain compounds | 0.01–0.04 ng/L | 58–70 | [25] |
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