Table 3.
Chemical Analyte Descriptive Statistics in Snart Foraeldre/Milieu Population and NHANES Population.a,b
Snart Foraeldre/Milieu | NHANESc | ||||||||||
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N | GM | 10th Pctl | 95th Pctl | % >LOD | Nc | GM | 10th Pctl | 95th Pctl | % >LOD | NHANES Year | |
Cotinine (ng/mL) | |||||||||||
Cotinine | 73 | 0.09 | 0.01 | 120 | 86 | 1216 | 36.58 | 0.011 | 258 | 100 | 11–12 |
Metals_Blood (ng/mL except lead which is μg/dL) | |||||||||||
Blood cadmium | 73 | 0.2 | 0.071 | 0.76 | 88 | 1234 | 0.46 | 0.11 | 1.57 | 84.12 | 11–12 |
Blood manganese | 73 | 10.52 | 7.66 | 17.65 | 100 | 1234 | 10.95 | 6.84 | 18.69 | 100 | 11–12 |
Blood lead | 73 | 0.81 | 0.53 | 1.58 | 100 | 1234 | 0.72 | 0.32 | 1.54 | 97.57 | 11–12 |
Blood selenium | 73 | 115.02 | 98.52 | 140 | 100 | 1234 | 192.0 | 162.88 | 234.96 | 100 | 11–12 |
Blood mercury, total | 73 | 1.59 | 0.69 | 5.2 | 97 | 1234 | 1.14 | 0.21 | 3.79 | 96.84 | 11–12 |
Metals (ng/mL) | |||||||||||
Barium | 50 | 0.68 | 0.17 | 2.7 | 100 | 410 | 1.57 | 0.29 | 4.34 | 98.54 | 11–12 |
Cadmium | 50 | 0.1 | 0.03 | 0.52 | 80 | 410 | 0.19 | 0.04 | 0.63 | 80.73 | 11–12 |
Cobalt | 50 | 0.28 | 0.07 | 1.06 | 100 | 410 | 0.55 | 0.10 | 1.58 | 98.78 | 11–12 |
Cesium | 50 | 2.97 | 0.95 | 10.6 | 100 | 410 | 4.39 | 1.13 | 10.8 | 100 | 11–12 |
Molybdenum | 50 | 25.98 | 5.54 | 134 | 100 | 410 | 47.01 | 9.04 | 121 | 100 | 11–12 |
Lead | 50 | 0.24 | 0.08 | 0.88 | 98 | 410 | 0.35 | 0.06 | 1.58 | 91.22 | 11–12 |
Antimony | 50 | 0.04 | 0.02 | 0.15 | 72 | 410 | 0.06 | 0.03 | 0.15 | 54.39 | 11–12 |
Tin | 46 | 0.16 | 0.06 | 0.63 | 65 | 410 | 1.00 | 0.16 | 4.04 | 79.02 | 11–12 |
Strontium | 50 | 79.69 | 22.06 | 333.39 | 100 | 410 | 107.94 | 20.04 | 282.98 | 100 | 11–12 |
Thallium | 50 | 0.15 | 0.04 | 0.46 | 100 | 410 | 0.18 | 0.05 | 0.44 | 99.27 | 11–12 |
Tungsten | 50 | 0.05 | 0.01 | 0.28 | 78 | 409 | 0.18 | 0.02 | 0.44 | 80.44 | 11–12 |
Uranium | 50 | 0 | 0 | 0.02 | 68 | 410 | 0.01 | 0.002 | 0.02 | 64.88 | 11–12 |
Arsenic, total | 57 | 9.25 | 1.9 | 48.34 | 100 | 410 | 14.77 | 1.83 | 54.90 | 94.15 | 11–12 |
Arsenic Metabolites (ng/mL) | |||||||||||
Arsenobetaine | 57 | 5.51 | 0.82 | 53.8 | 78 | 412 | 8.49 | 0.84 | 36.90 | 49.03 | 11–12 |
Dimethylarsonic acid | 57 | 2.93 | 1.35 | 7.46 | 69 | 412 | 4.53 | 1.27 | 11.40 | 76.7 | 11–12 |
Monomethylarsonic acid | 57 | 0.43 | 0.14 | 1.64 | 69 | 412 | 0.79 | 0.63 | 1.51 | 24.03 | 11–12 |
PAH Biomarkers (ng/L) | |||||||||||
1-hydroxynaphthalene | 56 | 309.32 | 72.81 | 5907.16 | 98 | 410 | 3806.53 | 248 | 19,250 | 100 | 11–12 |
1-hydroxyphenanthrene | 56 | 67.92 | 23.26 | 589.83 | 98 | 410 | 178.78 | 36 | 540 | 99.76 | 11–12 |
1-hydroxypyrene | 56 | 58.96 | 20.00 | 458.60 | 98 | 410 | 212.64 | 34 | 671 | 99.27 | 11–12 |
2-hydroxyfluorene | 56 | 95.32 | 24.68 | 865.00 | 100 | 410 | 512.62 | 49 | 2394 | 100 | 11–12 |
2-hydroxynaphthalene | 56 | 1158.68 | 237.54 | 15,869.08 | 100 | 410 | 9464.10 | 854 | 30,078 | 100 | 11–12 |
2-hydroxyphenanthrene | 56 | 30.94 | 7.07 | 230.47 | 88 | 410 | 86.93 | 17 | 246 | 96.83 | 11–12 |
3-hydroxyfluorene | 56 | 39.49 | 10.61 | 499.19 | 91 | 409 | 244.84 | 16 | 1257 | 97.07 | 11–12 |
3-hydroxyphenanthrene | 56 | 30.68 | 7.07 | 278.56 | 84 | 410 | 91.71 | 15 | 295 | 94.39 | 11–12 |
4-hydroxyphenanthrene | 56 | 13.73 | 7.07 | 99.37 | 46 | 409 | 30.17 | 7.1 | 96 | 75.79 | 11–12 |
9-hydroxyfluorene | 56 | 113.1 | 28.81 | 1178.22 | 100 | 410 | 409.88 | 47 | 1216 | 100 | 11–12 |
Brominated Flame Retardants (pg/g) | |||||||||||
PBDE153 | 73 | 6.43 | 3.6 | 14.2 | 95 | 363 | 66.47 | 8.6 | 319.1 | 92.56 | 03–04 |
PCBs (ng/g) | |||||||||||
PCB99 | 73 | 0.02 | 0.01 | 0.04 | 99 | 326 | 0.02 | 0.01 | 0.06 | 100 | 03–04 |
PCB138 & 158 | 73 | 0.11 | 0.05 | 0.28 | 100 | 332 | 0.07 | 0.02 | 0.18 | 100 | 03–04 |
PCB146 | 73 | 0.02 | 0.01 | 0.06 | 99 | 331 | 0.01 | 0 | 0.02 | 98.49 | 03–04 |
PCB153 | 73 | 0.16 | 0.07 | 0.39 | 100 | 331 | 0.08 | 0.02 | 0.22 | 100 | 03–04 |
PCB170 | 73 | 0.04 | 0.02 | 0.12 | 99 | 332 | 0.02 | 0.01 | 0.05 | 97.69 | 03–04 |
PCB178 | 73 | 0.01 | 0 | 0.03 | 82 | 331 | 0 | 0 | 0.01 | 71.3 | 03–04 |
PCB180 | 73 | 0.10 | 0.04 | 0.28 | 100 | 332 | 0.06 | 0.01 | 0.16 | 100 | 03–04 |
PCB183 | 73 | 0.01 | 0.01 | 0.03 | 96 | 332 | 0.01 | 0 | 0.02 | 87.95 | 03–04 |
PCB187 | 72 | 0.03 | 0.01 | 0.09 | 100 | 332 | 0.02 | 0 | 0.04 | 98.8 | 03–04 |
PCB194 | 73 | 0.01 | 0.01 | 0.04 | 25 | 322 | 0.01 | 0 | 0.04 | 78.26 | 03–04 |
PCB199 | 73 | 0.01 | 0.00 | 0.04 | 86 | 330 | 0.01 | 0 | 0.03 | 85.76 | 03–04 |
Persistent Pesticides (ng/g) | |||||||||||
Hexachlorobenzene | 73 | 0.06 | 0.04 | 0.1 | 100 | 36 | 0.05 | 0.04 | 0.07 | 100 | 07–08 |
p,p′-DDE | 73 | 0.18 | 0.09 | 0.62 | 99 | 36 | 1.14 | 0.41 | 2.63 | 100 | 07–08 |
Perchlorate (ng/mL) | |||||||||||
Perchlorate | 56 | 2.14 | 0.53 | 18.9 | 100 | 401 | 3.56 | 0.75 | 11.1 | 100 | 11–12 |
Phenols (ng/mL) | |||||||||||
Butyl Paraben | 56 | 0.29 | 0.53 | 1.58 | 63 | 409 | 3.31 | 0.14 | 16.2 | 46.21 | 11–12 |
benzophenone-3 | 56 | 3.64 | 0.14 | 211 | 86 | 409 | 462.61 | 10.4 | 2230 | 99.76 | 11–12 |
bisphenol A | 56 | 0.99 | 0.2 | 6.7 | 95 | 409 | 2.91 | 0.28 | 10.60 | 88.51 | 11–12 |
Methyl Paraben | 56 | 18.16 | 2.2 | 475 | 96 | 409 | 264.89 | 7.30 | 1120.0 | 100 | 11–12 |
Propyl Paraben | 56 | 1.67 | 0.07 | 228 | 86 | 409 | 80.65 | 1.20 | 309.0 | 99.27 | 11–12 |
Phthalates (ng/mL) | |||||||||||
Mono-n-butyl phthalate | 56 | 5.41 | 1.1 | 37.2 | 95 | 409 | 19.37 | 0.5 | 46.8 | 91.69 | 11–12 |
Mono-benzyl phthalate | 56 | 1.37 | 0.21 | 10.2 | 82 | 409 | 10.11 | 0.50 | 37.3 | 97.56 | 11–12 |
Mono(carboxynonyl) phthalate | 56 | 0.37 | 0.14 | 1.8 | 66 | 409 | 3.83 | 0.7 | 11.4 | 98.53 | 11–12 |
Mono(carboxyoctyl) phthalate | 56 | 2.3 | 0.5 | 20.2 | 96 | 409 | 59.67 | 4 | 248.9 | 100 | 11–12 |
Mono-(3-carboxypropyl) phthalate | 56 | 0.47 | 0.14 | 2.6 | 63 | 409 | 9.31 | 0.5 | 30.0 | 97.8 | 11–12 |
Mono–2-ethyl–5-carboxypentyl phthalate | 56 | 4.72 | 1.1 | 31.6 | 98 | 409 | 25.08 | 3.1 | 76.8 | 99.76 | 11–12 |
Mono–2-ethyl–5-hydroxyhexyl phthalate | 56 | 2.83 | 0.8 | 14.7 | 96 | 409 | 15.99 | 1.1 | 49.5 | 99.76 | 11–12 |
Mono–2-ethylhexyl phthalate | 56 | 0.75 | 0.35 | 4.1 | 95 | 409 | 3.87 | 0.35 | 9.7 | 75.06 | 11–12 |
Mono–2-ethyl–5-oxohexyl phthalate | 56 | 1.91 | 0.4 | 11.5 | 95 | 409 | 10.58 | 1.2 | 31.9 | 99.27 | 11–12 |
Monoethyl phthalate | 56 | 12.53 | 2.1 | 163 | 98 | 409 | 138.24 | 12.5 | 388.0 | 99.76 | 11–12 |
Mono-isobutyl phthalate | 56 | 11.72 | 1.8 | 138 | 100 | 409 | 11.71 | 1.2 | 35.1 | 98.53 | 11–12 |
Phytoestrogens (ng/mL) | |||||||||||
Daidzein | 56 | 34.75 | 2.6 | 791 | 98 | 497 | 462.34 | 6.5 | 1980 | 100 | 09–10 |
O-Desmethylangolensin | 56 | 0.99 | 0.14 | 35.3 | 88 | 497 | 121.86 | 0.3 | 597 | 94.16 | 09–10 |
Equol | 56 | 15.87 | 3.01 | 194 | 100 | 497 | 115.99 | 2.84 | 81.3 | 100 | 09–10 |
Enterodiol | 56 | 82.11 | 8.2 | 1440 | 100 | 497 | 157.17 | 5.17 | 553 | 99.4 | 09–10 |
Enterolactone | 56 | 836.79 | 141 | 8360 | 100 | 497 | 669.63 | 16.3 | 2610 | 100 | 09–10 |
Genistein | 56 | 6.96 | 0.5 | 245 | 98 | 497 | 217.07 | 3.2 | 545 | 100 | 09–10 |
Diakylphosphate Metabolites (ng/mL) | |||||||||||
Diethylphosphate | 55 | 0.55 | 0.07 | 5.67 | 75 | 425 | 3.53 | 3.53 | 14.7 | 31.06 | 07–08 |
Dimethylthiophosphate | 56 | 0.5 | 0.07 | 4.97 | 77 | 426 | 7.26 | 7.26 | 36.8 | 73.94 | 07–08 |
Organophosphates (ng/mL) | |||||||||||
3,5,6-trichloropyridinol | 56 | 0.66 | 0.07 | 5.59 | 88 | 482 | 1.34 | 0.07 | 4.02 | 80.71 | 09–10 |
Para-nitrophenol | 55 | 0.32 | 0.07 | 2.86 | 78 | 482 | 0.79 | 0.07 | 2.65 | 78.01 | 09–10 |
PFAS (ng/mL) | |||||||||||
Perfluorodecanoic acid | 73 | 0.27 | 0.2 | 0.5 | 100 | 375 | 0.24 | 0.07 | 0.64 | 80 | 11–12 |
Perfluorohexane sulfonic acid | 73 | 0.31 | 0.2 | 0.7 | 100 | 375 | 1.21 | 0.33 | 4.28 | 97.87 | 11–12 |
Perfluorononanoic acid | 73 | 0.58 | 0.3 | 1.1 | 100 | 375 | 0.93 | 0.37 | 2.07 | 99.73 | 11–12 |
Perfluorooctanoic acid | 73 | 1.55 | 0.7 | 3.9 | 100 | 375 | 1.88 | 0.75 | 3.15 | 100 | 11–12 |
Perfluorooctane sulfonic acid | 73 | 5.55 | 2.6 | 11.7 | 100 | 375 | 5.36 | 1.76 | 12.50 | 0 | 11–12 |
Biomarkers chosen for inclusion and if detected in over 60% of the population.
Results presented in volumetric concentrations.
The number of NHANES women included in analysis varied because of missing data, whether the biomarker was measured in a pooled subsample of the NHANES population and by sampling year. As a result, between 36 and 1234 women were included to obtain the NHANES concentrations for each biomarker. In the Danish study population, the number of women included in descriptive statistics analyses varied due to missing data.