Review Article
Analytical Methodologies for the Determination of Endocrine Disrupting Compounds in Biological and Environmental Samples
Table 3
Determination of alquilphenols in biological and environmental samples.
| Analytes | Samples | Extraction | Determination | Analytical parameters | Reference |
| Octyl, nonylphenol ethoxylates, and carboxylates | Wastewater | SPE, LLE | LC-MS2 | Recovery: 21–71% LODs: 2–29 ng·L−1 | [122] | APs, APEOs, APECs | Surface, wastewater | SPE | LC-MS2 | Recovery: 50–90% LODs: 1–100 ng·L−1 | [123] | OP, NP, and BPA | Bottled water | — | UHPLC-MS2 | Recovery: 97–106% LODs: 0.04–0.057 µg·L−1 | [124] | 4-t-Octylphenol, 4-nonylphenols, and bisphenol A | Fish liver | ASE | LC-MS | Recovery: 53% LODs: 5–20 ng·g−1 | [125] | Bisphenol A | Bovine milk | SPE | LC-MS | Recovery: 71–97% LOD: 0.20 μg·L−1 | [126] | Bisphenol A-diglycidyl ether, bisphenol F-diglycidyl ether, and their derivatives | Canned food and beverages | SPE | LC-MS2 | Recovery: 60–95% MQLs: 0.13–0.6 μg·L−1 MQLs: 1–4 μg·kg−1 | [127] | Nonionic surfactants | Wastewater | — | LC-QTOF-MS | MDLs: 10–200 µg·L−1 | [128] | APs, AP1-15EOs | Amended soil | PLE | LC-MS | Recovery: 36–110% LODs: 0.3–30 ng·g−1 | [129] | 4-Tert-octylphenol, 4-octylphenol, 4-n-nonylphenol, nonylphenol, and bisphenol A | Sea water | DLLME | LC-MS2 | Recovery: 90–108% MQLs: 0.005–0.03 μg·L−1 | [130] |
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LC: liquid chromatography; UHPLC: Ultra high-pressure liquid chromatography; TOF: time-of-flight; MS: mass spectrometry. SPE: solid-phase extraction; LLE: liquid-liquid extraction; PLE: pressurised liquid extraction; ASE: accelerated solvent extraction; DLLME: dispersive liquid-liquid extraction. MQL: method quantification limit; LOQ: limit of quantification; LOD: limit of detection; IDL: instrument detection limit. BPA: bisphenol A; NP: nonylphenol; OP: octylphenol; APs: alkylphenols; APEOs: alkylphenol polyethoxylates; OPEOs: octylphenol ethoxylates PE1C: nonylphenoxy carboxylate; NPE2C: nonylphenoxy ethoxy carboxylate.
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