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. 2021 Feb 21;22(4):2148. doi: 10.3390/ijms22042148

Table 2.

Biological effects provoked by long- and short-chain PFASs.

Category Study Type PFASs Results References
Endocrine disruption Odense Child Cohort (adults, n = 210) PFOS, PFOA, PFHxS, PFNA, PFDeA association between serum PFOS level and increased thyroid stimulating hormone;
positive association between repeated measures of serum PFNA and total T4 level in women
[41]
Cross-sectional (children, n = 85) PFOA, PFNA, PFUnA, PFDA disturbance of thyroid hormone homeostasis (differs between sexes) [42]
Obesity Cross-sectional (adults, n = 1612) PFOA, PFOS and other PFASs positive association between PFASs exposure with overweight and increased waist circumference (with particular emphasis on the effect of PFOA on selected obesity parameters) [43]
Odense Child Cohort (mother–child, n = 412) PFOS, PFOA each ln-unit increase in maternal serum PFOS and PFOA levels during pregnancy increased odds for overweight or/and obesity in children [44]
Odense Child Cohort (mother–daughter, n = 359) PFOA, PFOS, PFNA, PFHxS prenatal exposure to PFOA and PFOS was associated with girls % body fatness (except PFHxS and PFNA) [45]
Diabetes Cross-sectional (adults, n = 7904) PFOA serum PFOA was positively associated with diabetes in men;
PFOA disrupt cholesterol metabolism (at environmental relevant level)
[46]
Odense Child Cohort (adults, n = 4129) PFOA no association between PFOA exposure and incidence of diabetes [47]
Reproductive disorders Case-control (adult women, n = 367) PFOS, PFOA, PFBS, PFHxS, PFNA, PFDA and other association between plasma PFDA level and significantly increased risk of PCOS-related infertility [48]
In vitro (primary human placental cytotrophoblasts) PFOS apoptosis of human placental syncytiotrophoblasts) [49]
Odense Child Cohort (couples, n = 501) PFOA, PFOS, PFNA, PFOSA, PFDeA and other associations between two perfluoroalkyl substances and menstrual cycle length changes (2–5% shorter menstrual cycles during PFOA exposure and 3% longer during PFDeA exposure); association between selected perfluoroalkyl substances and lower pregnancy probability [50]
Breast cancer Odense Child Cohort (adult women, n = 388) PFOS, PFOA positive association between high concentrations of PFOS and breast cancer risk (for analyses that were restricted to expression of estrogen receptors: ER+/PR+ tumors) [51]
Hepatotoxicity Odense Child Cohort (adults, n = 1605) PFOA, PFOS, their isomers and other clinically significant hepatic cell dysfunction (abnormal liver function biomarkers: prealbumin and ALT level) [52]
Cross-sectional (adults, n = 1016) PFOA, PFOS, PFOSA, PFNA, PFDA, PFHxS and other positive association between the changes in activity of ALT, ALP, and GGT after PFASs exposure and changes in circulating bilirubin level [53]
Cross-sectional (adults, n = 30,723) PFOA association between PFOA and ALT,
a marker of hepatocellular damage but no evidence that PFOA increases the risk of clinically diagnosed liver disease
[54]
Nephrotoxicity Odense Child Cohort (adults, n = 1612) PFOA, PFOS negative association between PFASs exposure (except for PFOA and PFDA) and estimated glomerular filtration rate (eGFR) and positive association with chronic kidney disease (CKD) [55]
Asthma Cross-sectional (children, n = 456) PFOS, PFOA, PFBS, PFDA, PFNA, PFHxS and other significant inverse association between serum PFASs and CC16 (club cell secretory protein; biomarker of asthma) levels in asthmatics [56]
Cross-sectional (children, n = 300) PFOA, PFOS positive association between serum PFASs level and impaired lung function in children (association was significant only in asthmatic children) [57]
Immunotoxicity Cross-sectional (adult, n = 733) PFOA, PFOS, PFHxS, PFNA, PFDA and other strong positive associations between blood PFOS level and leucocyte telomere length [58]
Odense Child Cohort(mother–child,
n = 349)
PFOS, PFHxS, PFOA, PFNA, PFDA deficient antibody responses in children prenatally exposed to PFASs [59]

PFUnA, perfluoroundecanoic acid; PFDeA, perfluorodecanoic acid.