Table 1.
Study | Exposure | Association | |||||||
---|---|---|---|---|---|---|---|---|---|
Reference | Design | Location | Sample size | Timing | Assessment | Chemical | Level | Modeled Exposure | HR/OR/RR (95% CI) |
Eslami 2016 | Case-control | Tehran, Iran | N=115 nPE=45 |
3rd trimester | Serum (ng/g lipid) | Total PCB | PE: 3.72 (2.37) Control: 2.07 (1.66) |
Not reported | OR: 1.77 (1.34, 2.32) |
Total PBDE | PE: 2.15 (1.64) Control: 1.20 (0.90) |
2.19 (1.39, 3.45) | |||||||
Total POP | PE: 5.87 (3.54) Control: 3.28 (2.23) |
1.54 (1.26, 1.87) | |||||||
Murray 2018 | Retrospective cohort | South Africa | N=633 nPE=15 |
Delivery | Serum (ng/g lipid) | p,p’-DDT | 52.5 (18.6, 257.1)† | Per ln-unit | OR: 1.26 (0.74, 2.16) |
p,p’-DDE | 239.0 (88.7, 878.1)† | 1.14 (0.62, 2.10) | |||||||
o,p’-DDT | 7.0 (3.4, 22.6)† | 1.48 (0.86, 2.56) | |||||||
Savitz 2014 | Retrospective cohort | U.S. | N=1,933 nPE=131 |
Every 8 weeks after enrollment; analysis used 3rd trimester samples | Serum (µg/l) | p,p’-DDT | 9.25 (6.22, 14.19)† | Upper vs. lowest quintile | OR: 0.6 (0.2, 1.5) |
p,p’-DDE | 24.50 (16.95, 36.73)† | 0.8 (0.4, 1.8) | |||||||
Total PCB | 2.69 (1.85, 3.83)† | 0.5 (0.2, 1.3) | |||||||
β-HCH | 1.39 (1.01, 2.11)† | 1.2 (0.5, 3.2) | |||||||
Savitz 2012 | Cross-sectional | Mid-Ohio Valley, US | N=10,189 nPE=730 |
Measured in 2005–2006 and modeled 15 years prior | Estimated serum (ng/ml) | PFOA | Exposure year 1990–1994: 6.0 (4.5, 27.6)† 1995–1999: 10.7 (5.1, 50.4)† 2000–2005: 15.9 (5.9, 56.2)† |
IQR (lnPFOA) | OR: 1.13 (1.00, 1.28) |
Stein 2009 | Cross-sectional | Mid-Ohio Valley, US | N=1,589 nPE=156 |
Measured in 2005–2006 and included pregnancies from 2000–2006 | Serum (ng/ml) | PFOA | 21.2 (10.3, 49.8)† | ≥50th percentile vs. <50th percentile | OR: 1.3 (0.9, 1.9) |
N=4,566 nPE=407 |
PFOS | 13.6 (9.4, 18.7)† | 1.3 (1.1, 1.7) | ||||||
Starling 2014 | Case-cohort | Norway | N=976 nPE=466 |
2nd trimester | Plasma (ng/ml) | PFOA | 2.78 (2.14, 3.57)† | Per ln-unit | HR: 0.89 (0.65, 1.22) |
PFNA | 0.54 (0.39, 0.74)† | 0.90 (0.70, 1.16) | |||||||
PFDA | 0.10 (<LOQ, 0.18)† | 0.88 (0.75, 1.04) | |||||||
PFUnDA | 0.17 (0.08, 0.27)† | 0.78 (0.66, 0.92) | |||||||
PFHxS | 0.69 (0.49, 0.95)† | 0.91 (0.72, 1.14) | |||||||
PFHpS | 0.15 (0.09, 0.23)† | 1.03 (0.86, 1.24) | |||||||
PFOS | 12.87 (9.69, 17.03)† | 1.13 (0.84, 1.52) |
Abbreviations: hazard ratio (HR); odds ratio (OR); risk ratio (RR); confidence interval (CI); interquartile range (IQR); preeclampsia (PE); polychlorinated biphenyls (PCB); polybrominated diphenyl ethers (PBDE); persistent organic pollutants (POP); dichlorodiphenyltrichloroethane (DDT); dichlorodiphenyldichloroethylene (DDE); beta-hexachlorocyclohexane (HCH); perfluorooctanoic acid (PFOA); perfluorooctane sulfonic acid (PFOS); perfluorononanoic acid (PFNA); perfluorodecanoic acid (PFDA); perfluoroundecanoic acid (PFUnDA); perfluorohexane sulfonate (PFHxS); perfluoroheptane sulfonate (PFHpS)
Note. Levels represent mean (standard deviation), or median (IQR).