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. 2021 Apr 15;19(1):1229–1247. doi: 10.1007/s40201-021-00656-3

Table 1.

Extraction techniques of various congeners of polybrominated diphenyl ethers

Congener Sample matrix Extraction mode Analysis Concentration Reference
28 sediment SE b 0.002 ng/g dw-0.251 ng/g dw [70]
soil SE a 0.78 ng/g dw-5.15 ng/g dw [15]
soil PLE b <LOD-0.04 ng/g dw [33]
sewage sludge UAE c 1.12 ± 0.03 ng/g [191]
human serum UAE d <LOD-0.74 ng/g [192]
Fish and mussels UAE d 0.04 ng/g ww-0.358 ng/g dw [88]
human semen e 2.282 pg/g ww-8.28 pg/g ww [78]
human blood centrifugation e 5.74 pg/g ww-15.1 pg/g ww [78]
47 sediment SE b 0.012 ng/g dw-0.365 ng/g dw [70]
sediment USE d 190 ± 10–780 ± 60 pg/g dw [193]
sewage sludge UAE c 38.6 ± 1.6 ng/g [191]
human serum UAE d 0.84 ng/g-1.89 ng/g [192]
Water sample SPE d 15–205 pg/L [193]
Soil PLE b 0.23–0.39 ng/g dw [33]
human semen e 4.32 pg/g ww-9.32 pg/g ww [78]
blood sample centrifugation e 8.54 pg/g ww-18.0 pg/g ww [78]
fish and mussels USE d 0.09 ng/g ww-1.73 ng/g dw [88]
wastewater SPME f 134 ± 19 [96]
Milk SPME f 12.7 ± 2.2–32.0 ± 3.2 [96]
Sludge from WWTP USE a 8–90 ng/g dw [147]
66 sediment SE a 0.80 ng/g dw [15]
71 sediment SE a 2.27 ng/g dw [15]
soil SE a 1.93 ng/g dw −16.1 ng/g dw [15]
99 sediment SE a 6.87 ng/g dw [15]
sediment SE b 0.011 ng/g dw-0.491 ng/g dw [70]
sediment USE d 340 ± 40–2990 ± 390 [193]
soil SE b 13.3 ng/g dw-615 ng/g dw [15]
sewage sludge UAE c 29.3 ± 0.7 [191]
human serum UAE d <LOD-1.64 ng/g [192]
Water sample SPE d 13–181 pg/L [193]
Soil PLE b 0.26–0.55 ng/g dw [35]
human semen e 2.25 pg/g ww-7.47 pg/g ww [78]
human blood centrifugation e 1.52 pg/g ww-7.55 pg/g ww [78]
fish and mussels USE d <LOD-0.402 ng/g dw [88]
wastewater SPME f 155 ± 20 [96]
milk SPME f nd −135 ± 11 [96]
Sludge from WWTP USE a 18–33 ng/g dw [147]
100 sediment SE b 0.005 ng/g dw [70]
sediment 92 ± 10–540 ± 80 pg/g dw [193]
soil SE a 2.70 ng/g dw-89.4 ng/g dw [15]
Soil PLE b 0.09–0.16 ng/g dw [35]
fish and mussels USE d 0.09 ng/g ww-0.387 ng/g dw [88]
sewage sludge UAE c 8.1 ± 0,2 ng/g [191]
human serum UAE d <LOD-1.48 ng/g [192]
Water sample SPE d 4–29 pg/L [193]
human semen e <LOD-0.517 pg/g ww [78]
human blood centrifugation e <LOD-2.66 pg/g ww [78]
wastewater SPME f 147 ± 10 [96]
milk SPME f Nd-34.4 ± 5.2 [96]
138 soil SE a 2.35 ng/g dw −9.91 ng/g dw [15]
139 soil SE a 3.56 ng/g dw-39.9 ng/g dw [15]
153 sediment SE b 0.001 ng/g dw-0.281 ng/g dw [70]
sediment USE d 70 ± 10–130 ± 30 pg/g dw [193]
soil SE a 44.1 ng/g dw −210 ng/g dw [15]
fish and mussels USE d <LOD-0.221 ng/g dw [88]
sewage sludge UAE c 7.3 ± 0.4 ng g [191]
human serum UAE d <LOD-2.61 ng/g [192]
Water sample SPE d 6–38 pg/L [192]
Soil PLE b 0.04–0,12 ng/g dw [35]
human semen e <LOD-6.37 pg/g ww [78]
human blood centrifugation e 10.7 pg/g ww-25.6 pg/g ww [78]
154 sediment SE b 0.002 ng/g dw-0.541 ng/g dw [70]
sediment USE d 50 ± 10–100 ± 10 PG/G dw [193]
soil SE a 32.0 ng/g dw-48.9 ng/g dw [15]
Soil PLE b <LOD-0.08 [35]
fish and mussels USE d <LOD-0.317 ng/g dw [88]
sewage sludge UAE c 5.3 ± 0.2 ng/g [191]
human serum UAE d <LOD-1.46 ng/g [192]
human semen e <LOD-0.734 pg/g ww [78]
human blood centrifugation e <LOD-2.45 pg/g ww [78]
wastewater SPME f 215 ± 4 ng/L [96]
milk SPME f Nd-225 ± 20 ng/L [96]
Water sample SPE d 4–25 pg/g [193]
183 sediment SE b 0.019 ng/g dw-0.911 ng/g dw [70]
sediment USE d 20 ± 10–90 ± 20 pg/g dw [193]
soil SE a 22.3 ng/g dw- 824 ng/g dw [15]
Soil PLE b <LOD-0.24 ng/g dw [35]
human semen e <LOD-1.06 pg/g ww [78]
human blood centrifugation e 0.193 pg/g ww −4.54 pg/g ww [78]
Water sample SPE d 3–32 pg/L [193]
209 human semen e <LOD-18.2 pg/g ww [78]
human blood centrifugation e 25.3 pg/g ww −61.3 pg/g ww [78]
Sludge from WWTP USE a Nd- 1135 ng/g dw [147]
Water sample SPE d 770–3810 pg/L [193]
sediment USE d 2130 ± 270–10,600 ± 1200 [193]
sediment soxhlet a 0.781 ng/g-8.95 ng/g dw [70]

a – GC-MS/MS; b – GC-MS; c – GC-ICP; d – GC-ICP-MS; e – GC-MS NCI with SIM; f - GC-ECD