Table 4.
Type of Bispheno |
Study Design |
Study Population (Age) (Project Name) |
Country (Sample Population) | Biological Sample | [Bisphenol] Detected in Biological Sample (Mean/ Median) |
Findings | Beta Coefficient |
Significant Values | Author |
---|---|---|---|---|---|---|---|---|---|
BPA | Cross sectional study | Male children (6–11 y.o) Male Adolescents (12–19 y.o) (NHANES Project) |
USA (n = 588) | Urine Serum | Mean: male children 1.74 ng/mL (urine) Mean: male adolescents 1.94 ng/mL (urine) |
Reproductive hormones: No association between BPA and reproductive hormones in male children across the quartiles. Increased BPA level caused a significant decrease in TT in male adolescents across the quartiles. |
Q2: β = −49.34% Q3: β = −36.87% Q4: β = −53.70% |
p < 0.05 | [108] |
BPA | Cross sectional study | Male worker of epoxy resin manufacturer (16–63 y.o) |
Shanghai, China (n = 592) | Urine Serum | Median occupational exposure: 685.9 µg/g Cr (urine) Median non-occupational exposure: 4.2 µg/gCr (urine) |
Reproductive hormones: Increased level of BPA cause significant increase in:
Increased level of BPA cause significant decreased in levels:
|
[109] | ||
β = 0.0589 ng/mL | p < 0.001 | ||||||||
β = 0.0293 nmol/L | p < 0.01 | ||||||||
β = 0.0362 pg/mL | p < 0.001 | ||||||||
β = −0.0367 ng/mL | p < 0.001 | ||||||||
β = −0.024 mIU/mL | p < 0.05 | ||||||||
BPA | Cross sectional study | Male worker of epoxy resin manu-facturer | Guang-dong, China (n = 559) | Serum | Median workers: 8.75 ng/mL (serum) Median non-workers: 3.37 ng/mL (serum) |
Reproductive hormones: No association between workers and non-workers on the level of SHBG, TT, INB and AD |
[110] | ||
Increased exposure time caused significant decreased in median AD level among workers. | - | p < 0.001 | |||||||
Increased exposure time caused significant increase in median SHBG level among workers. | - | p < 0.05 | |||||||
Increased BPA level caused significant increase in median SHBG level among workers. | β = 2.79 nmol/L | p < 0.05 | |||||||
Increased of BPA level caused significant decreased in median AD level among workers. | β = −0.18 ng/mL | p < 0.001 | |||||||
BPA | Cross sectional study | Young men | Denmark (n = 308) |
Urine Serum Semen |
Median: 3.74 ng/mL (Osm)(urine) |
Reproductive hormones: Increased level of BPA caused significant increase in:
|
[111] | ||
β = 0.7 nmol/L | p < 0.01 | ||||||||
β = 2.7% | p < 0.05 | ||||||||
β = 3.5% | p < 0.05 | ||||||||
β = 2.7% | p < 0.05 | ||||||||
Sperm characteristics: Increased level of BPA caused a significant decreased in percentage of progressive motile spermatozoa across the quartiles. |
β = −1.82% | p < 0.01 | |||||||
BPA | Cross sectional study | Young men (18–23 y.o) |
Spain (n = 215) |
Urine Serum Semen |
Mean: 1.8 µg/g (urine) |
Reproductive hormones: Increased level of BPA caused significant increase in LH level across the quartiles. No association between BPA and FSH, FT, SHBG, INB and E2 across the quartile. |
β = 0.07 IU/L | p < 0.01 | [112] |
Sperm characteristics: Increased level of BPA caused significant decreased in sperm characteristic across the quartiles:
|
|||||||||
β = −0.04 Mill./mL | p < 0.01 | ||||||||
β = −0.05 Mill. | p < 0.01 | ||||||||
BPA | Retro-spective cohort | Pregnant woman Male chil-dren (8–14 y.o) (ELEMENT project) |
Mexico (n = 118) |
Urine Urine Serum |
Mean: 0.7 ng/mL (urine) Mean: 1.1 ng/mL (urine) |
Reproductive hormones: No association between prenatal urinary BPA and the boy sex hormones in the level of SHBG, INB, TT, E2, DHEAS and FT |
- | - | [114] |
No association between child-hood urinary BPA and the boy sex hormones in the level of SHBG, INB, TT, E2, DHEAS and FT | - | - | |||||||
BPA | Retro-spective cohort | Pregnant woman (Week 18 & 34) Young men (20–22 y.o) |
Australia (n = 423) |
Serum (mother) Semen |
Median: 0.25 µg/L (serum) | Sperm characteristics: Maternal exposure of BPA caused significant changes in sperm characteristics of young men such as increased in the sperm concentration and motility. |
- | p < 0.05 | [115] |
BPA | Pro-spective cohort |
Men IVF patient (34.05 y.o) |
Slovenia (n = 149) |
Semen | Mean: 1.33 ng/mg (urine) | Sperm characteristics: Increase concentration of BPA cause significant decrease in:
|
[116] | ||
β = −0.219, R2 = 0.071 | p = 0.047 | ||||||||
β = −0.241, R2 = 0.092 | p = 0.039 | ||||||||
β = −0.273, R2 = 0.075 | p = 0.043 | ||||||||
β = −0.266, R2 = 0.052 | p = 0.026 | ||||||||
BPA | Pro-spective cohort | Fertile men (>18 y.o) |
Michigan and Texas (n = 418) |
Urine Semen |
Mean: 0.51 µg/g (urine) | Sperm characteristics: Increased level of BPA caused significant decreased in sperm DNA fragmentation. No association between BPA and semen analysis (sperm morphology, sperm concentration, total sperm count, semen volume). |
β = −0.0544 | p < 0.05 | [118] |
BPA/ BPF/ BPS |
Cross sectional study |
Young men (18–20 y.o) FEPOS |
Denmark (n = 556) |
Urine Semen |
BPA (urine) Q1: <0.68 ng/mL Q3: 1.3–2.74 ng/mL BPF (urine) Q1: <0.06 ng/mL Q3: 0.14–0.34 ng/mL BPS Q1: <0.03 ng/mL Q3: 0.06–0.17 ng/mL (urine) |
Sperm characteristics: Percentage of motile spermatozoa in Q3 is significantly higher compared to Q1 in BPA and BPF exposures. Volume of semen per ejaculate in Q3 is significantly lower compared to Q1 in BPA and BPS exposures. No association between (BPA, BPF, and BPS) with the other semen analysis (sperm concentration, total sperm count, normal sperm morphology, motility and ejaculate volume). |
β = 1.07% β = −0.87 mL |
p < 0.05 p < 0.05 |
[119] |
BPS | Cross sectional study |
Infertile patient (18–56 y.o) |
Boston, MA, USA (n = 158) |
Urine Semen |
Mean BPA: 0.77 µg/L (urine) Mean BPS: 0.37 µg/L (urine) |
Semen characteristics: Volume of semen per ejaculate in Q2 is significantly higher compared to Q1 in BPS exposure. Sperm concentration in Q3 is significantly lower compared to Q1 in BPS exposure. Increased level of BPS caused significant decreased in sperm quality among obese/overweight men (BMI >25 kg/m2):
|
β = 3.0 mL β = −29.2 mil/mL |
p < 0.05 p < 0.05 |
[117] |
Abbreviations: ↑: Increase; ↓ Decrease