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. Author manuscript; available in PMC: 2022 Oct 19.
Published in final edited form as: Environ Sci Technol. 2021 Sep 30;55(20):14000–14014. doi: 10.1021/acs.est.1c02549

Table 1.

Percent detection and distribution of plasma concentrations of PCBs, PBDEs, OCPs and PFAS at baseline in 749 SELF participants (2010-2012) included in this analysis and NHANES serum samples for non-Hispanic Black and non-Hispanic White females aged 20-39 years from the 2009-2010 survey year.25

SELF participants NHANES non-Hispanic Black femalesa NHANES non-Hispanic White femalesa

Percent detected (%), all participants (N= 749) Arithmetic Mean Concentration (SD) Median Concentration (Range) 90th Percentile Mean 2009-2010 (SE) Mean 2009-2010 (SE)
PBDEs, ng/g d
  PBDE 17 12.6 NCb NCb NCb NCb NCb
  PBDE 28 92.7 1.14 (1.27) 0.82 (0.10 – 15.21) 2.04 1.37 (0.08) 0.81 (0.08)
  PBDE 47 97.3 26.50 (35.70) 16.50 (0.51 – 348.21) 51.60 36.3 (2.3) 15.2 (1.6)
  PBDE 66 9.0 NCb NCb NCb NCb NCb
  PBDE 99 96.3 5.69 (9.97) 3.01 (0.16 – 109.60) 11.40 8.51 (0.96) 2.74 (0.48)
  PBDE 100 97.2 5.42 (6.80) 3.25 (0.11 – 58.75) 11.10 7.49 (0.98) 3.52 (0.44)
  PBDE 153 97.3 7.86 (11.80) 4.44 (0.64 – 155.70) 16.00 10.1 (2.8) 13.2 (3.0)
  PBDE 209 71.7 2.61 (7.50) 1.63 (0.54 – 169.70) 3.84 2.22 (0.18) 2.27 (0.48)
PCBs, ng/g d
  PCB 28 80.8 0.98 (0.92) 0.79 (0.17 – 13.53) 1.57 NCb NCb
  PCB 66 78.4 0.53 (0.45) 0.42 (0.13 – 7.00) 0.91 NCb NCb
  PCB 74 97.1 1.69 (1.00) 1.47 (0.41 – 11.52) 2.68 1.69 (0.22) 1.97 (0.1)
  PCB 99 96.9 2.06 (1.67) 1.68 (0.32 – 23.49) 3.47 2.07 (0.28) 1.83 (0.11)
  PCB 105 92.7 0.93 (1.12) 0.69 (0.13 – 22.02) 1.62 0.69 (0.11) 0.65 (0.05)
  PCB 114 20.7 NCb NCb NCb NCb NCb
  PCB 118 99.5 3.53 (3.41) 2.76 (0.73 – 56.59) 5.88 2.94 (0.45) 2.97 (0.18)
  PCB 138/158 99.3 5.43 (4.02) 4.30 (0.71 – 51.68) 9.99 6.56 (0.92) 6.31 (0.4)
  PCB 146 92.7 0.94 (0.74) 0.73 (0.11 – 6.09) 1.81 1.23 (0.24) 0.94 (0.06)
  PCB 153 99.2 7.15 (4.92) 5.78 (1.06 – 39.80) 13.30 8.93 (1.48) 8.59 (0.56)
  PCB 156 89.7 0.77 (0.60) 0.60 (0.12 – 7.27) 1.40 0.96 (0.16) 1.16 (0.08)
  PCB 157 24.2 NCb NCb NCb NCb NCb
  PCB 167 44.1 NCb NCb NCb NCb NCb
  PCB 170 93.5 1.51 (1.13) 1.17 (0.17 – 8.71) 2.90 2.08 (0.43) 2.02 (0.13)
  PCB 178 54.6 NCb NCb NCb NCb NCb
  PCB 180 96.3 3.84 (3.01) 2.87 (0.47 – 24.32) 7.38 4.76 (0.81) 5.24 (0.34)
  PCB 183 85.3 0.66 (0.53) 0.52 (0.11 – 4.79) 1.26 1.08 (0.17) 0.72 (0.05)
  PCB 187 93.1 1.75 (1.50) 1.33 (0.17 – 12.76) 3.30 2.41 (0.51) 1.91 (0.13)
  PCB 194 82.5 0.71 (0.55) 0.56 (0.12 – 4.46) 1.37 1.06 (0.20) 1.08 (0.08)
  PCB 196/203 90.7 0.93 (0.67) 0.76 (0.12 – 5.06) 1.70 1.09 (0.20) 1.13 (0.08)
  PCB 199 81.5 0.86 (0.73) 0.67 (0.12 – 5.61) 1.62 1.21 (0.29) 1.09 (0.08)
  PCB 209 18.8 NCb NCb NCb NCb NCb
OCPs, ng/g d
  Hexachlorobenzene 68.6 6.29 (1.87) 5.94 (1.70 – 17.20) 8.62 6.41 (0.27) 7.57 (0.25)
  Oxychlordane 85.8 2.29 (1.04) 2.13 (0.59 – 7.40) 3.63 NCb NCb
  p-p’-DDE 97.3 57.80 (28.80) 51.40 (12.60 – 295.90) 92.00 110.0 (15.0) 86.3 (6.3)
  p-p’-DDT 48.3 NCb NCb NCb 2.98 (0.56) 2.72 (0.32)
  o-p’-DDT 2.4 NCb NCb NCb NCb NCb
  Trans-nonachlor 88.8 2.81 (1.65) 2.44 (0.62 – 16.61) 4.50 6.82 (0.50) 6.25 (0.5)
  β-HCH 62.1 NCb NCb NCb 2.19 (0.5) NCb
  γ-HCH (Lindane) 1.1 NCb NCb NCb NCb NCb
  Mirex 4.8 NCb NCb NCb NCb NCb
PFAS, ng/ml e
  PFOAc Linear: 99.2
Branched: 13.4
1.22 (1.75) 1.27 (0.14, 21.30) 2.27 1.19 (1.69) 2.44 (1.80)
  PFOSc Linear: 99.6
Branched: 98.9
3.99 (1.93) 4.10 (0.14, 47.60) 8.46 4.60 (1.73) 6.00 (1.93)
  PFDA 84.1 0.23 (0.16) 0.20 (0.07 – 1.90) 0.40 0.24 (1.55) 0.21 (1.86)
  PFHxS 97.7 0.80 (0.84) 0.60 (0.07 – 9.90) 1.50 0.71 (1.79) 0.95 (2.28)
  PFNA 99.2 0.59 (0.32) 0.52 (0.07 – 4.70) 0.90 1.02 (1.35) 0.14 (2.04)
  PFUA 44.1 NCb NCb NCb 0.15 (1.93) 0.21 (1.86)
a

Geometric means were calculated for PFAS for individual samples and arithmetic means were calculated for pooled PCBs, PBDEs, and OCPs, where pooled data are comparable to an arithmetic means of individual samples.

b

Mean not calculated due to high number of samples below the limit of detection.

c

Total PFOA and PFOS, including all isomers, means calculated for SELF and NHANES.

d

Concentrations are lipid adjusted.

e

Geometric standard deviations were calculated for PFAS in NHANES.