Table II.
Study | Contaminant | Outcome | Population | Results* |
---|---|---|---|---|
Mocevic (53) | Hg | Semen quality and reproduc. hormones | Male partners of pregnant women (n=194) | Inhibin B: Positive association (β=0.074, 95% CI: 0.021–0.126) No association with other semen characteristics or reproductive hormones |
Kvist (54) | PFOA and PFOS | Sperm Y:X ratio | Male partners of pregnant women (n=201) (participation rate: 78.5%) |
PFOS
|
Krüger (37) | PCBs and OCPs | ER, AR and AhR function | Men and women (n=247) (participation rate: 41% of all Greenlandic AMAP population and 74% for XAR and XARcompoutcomes) |
ΣPCBs
ER transactivity (males): Inverse association (β=−0.34 for XER)
|
Krüger (38) | PCBs and OCPs | ER and AR transactivity | Men and women (n=240) (participation rate: 82% for XAR/XER outcome) |
ΣPCBs
ΣOCPs
|
Bonde (43) | PCBs and p,p′-DDE | Fertility and markers of male reproductive function | Pregnant women and their spouses (n=598) (participation rate: 90%) |
PCB-153
|
p,p′-DDE
|
||||
Krüger (50) | POPs (evaluated as effects on ER, AR and AhR) | Sperm chromatin integrity | Male spouses of pregnant women (n=53) |
|
Long (39) | PCBs and OCPs | AhR transactivity | Men and women 18–77 years of age (n=357) (participation rate: 48% for AhRcompoutcome) |
ΣPCBs:
ΣOCPs
|
Krüger (40) | PCBs and p,p′-DDE | Serum xenoandrogenic activity | Male spouses of pregnant women (n=37) | PCB-153: No association
|
Toft (52) | POPs (evaluated as effects on ER, AR and AhR) |
Semen quality | Male spouses of pregnant women (n=54) | No association specifically in Inuit. When data combined across all 4 populations (Warsaw, Greenland, Kharkiv, Sweden), ER activity associated with increase in sperm concentration and motility. |
Long (51) | POPs (evaluated as effects on ER, AR and AhR) | Sperm DNA damage and Sperm apoptotic markers |
Male spouses of pregnant women (n=54) | DNA damage: Inverse association with ER and AhR Bcl-xL marker: Inverse association with AR (Spearman’s correlation=−0.46) No association with the sperm apoptotic marker, Fas |
Long (41) | PCBs and p,p′-DDE | AhR activity | Males (n=75) | PCB-153: No association p,p′-DDE: No association |
Stronati (45) | PCBs and p,p′-DDE | Sperm DNA fragmentation and sperm apoptotic markers | Male spouses of pregnant women (n=200) (participation rate: 79%) |
PCB-153: No association p,p′-DDE: No association |
Elzanaty (47) | PCBs and p,p′-DDE | Epididymal function and Accessory sex gland function |
Male spouses of pregnant women (n=163) | PCB-153
p,p′-DDE: No association |
Giwercman (48) | PCBs and p,p′-DDE | Reproductive hormone levels | Male spouses of pregnant women (n=258) (participation rate: 79%) |
PCB-153
p,p′-DDE
|
Bonefeld-Jorgensen (42) | PCBs and p,p′-DDE | Serum xenoestrogenic activity | Male spouses of pregnant women (n=72) | PCB-153: No association p,p′-DDE: Inverse association (Spearman’s correlation=−0.29 for XER) |
Tiido (49) | PCBs and p,p′-DDE | Sperm Y:X ratio | Male spouses of pregnant women (n=157) | PCB-153: No association p,p′-DDE: No association |
Toft (44) | PCBs and p,p′-DDE | Fertility | Pregnant women (n=598) and their spouses (n=201) (participation rate: 87%) |
PCB-153: No association p,p′-DDE: No association |
Spanò (46) | PCBs and p,p′-DDE | Sperm chromatin integrity | Male spouses of pregnant women (n=193) | PCB-153: No association p,p′-DDE: No association |
AhR=aryl hydrocarbon receptor; AMAP=Arctic Monitoring Assessment Programme; AR=androgen receptor; CI=confidence interval; DDE=dichlorodiphenyldichloroethylene; DNA=deoxyribonucleic acid; ER=oestrogen receptor; Hg=mercury; IU=international unit; LH=luteinizing hormone; MD=mean difference; OCPs=organochlorine pesticides; PCBs=polychlorinated biphenyls; PFOA=perfluorooctanoic acid; PFOS=perfluorooctanesulfonate; POPs=persistent organic pollutants; PSA=prostate specific antigen.
Adjusted estimates are presented where available. Presented estimates are statistically significant at p≤0.05 level.