Review Article
Analytical Methodologies for the Determination of Endocrine Disrupting Compounds in Biological and Environmental Samples
Table 4
Determination of flame retardants in biological and environmental samples.
| Analytes | Samples | Extraction | Determination | Analytical parameters | Reference |
| 38 HFRs | Wastewater | Preconditioned empire speed disk | LC–MS2 | Recoveries: 25–132% LOQs: 0.1–5.6 μg·L−1 | [131] | TBBPA and five PBDEs | Wastewater, river, and drinkingwater | LLE | LC-LIT | Recoveries: 43–99% LOQs: 0.2–3.3 ng·L−1 | [132] | HBCD isomers | Suspended sediments from detroit river | ASE | LC-MS2 | — | [133] | HBCD diastereoisomers | Marine sediment | MAE | LC-IT | Recoveries: 68–91% LOQs: 25–40 pg·g−1 | [134] | TBBPA and brominated BPA analogues | Sediment and sludge | Soxhlet | LC-MS2 | Recoveries: 70–105% LOQs: 0.02–0.15 ng·g−1 | [135] | TBBPA, BPA, MonoBBPA, DiBBPA, and TriBBPA | Sewage sludge and sediment | Sonication SPE | LC-MS-LIT | Recoveries: 39–120% LODs: 0.6–2.7 ng·g−1 | [136] | HBCDs and TBBPA | Sewage sludge | PLE | UHPLC-MS2 | Recoveries: 65–112% LOQs: 0.005–0.14 ng·g−1 | [137] | HBCDs (α-, β-, and γ-HBCD) | Food | MSPD | LC-MS2 | LODs: 1.5–4.3 ng·mL−1 | [138] | 36 halogenated flame retardants | Fish | PLE | LC-MS2 | IDLs: 4.7 pg | [139] |
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LC: liquid chromatography; UHPLC: ultra high-pressure liquid chromatography; MS: mass spectrometry; IT: ion trap; LIT: lineal ion trap. SPE: solid-phase extraction; ASE: assisted solvent extraction; LLE: liquid-liquid extraction; PLE: pressurised liquid extraction; MAE: microwave-assisted extraction; MSPD: matrix solid-phase dispersion. LOQ: limit of quantification; LOD: limit of detection; IDL: instrument detection limit. HFRs: halogenated flame retardants; BPA: bisphenol A; TBBPA: tetrabromobisphenol A; PBDEs: polybrominated dipheny lethers; HBCD: hexabromocyclododecanes.
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