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. 2020 May 11;176(2):253–284. doi: 10.1093/toxsci/kfaa065

Table 1.

Bisphenols and the Gut Microbiome

Chemical Exposure Window Dose Model Sex & Sex Differences Effect on Gut Microbiota Conclusions References
BPA Developmental 0, 0.2, 0.6, 1.7, 2.9, 5.7, 11.5, 23.0, or 45.0 µM in water environment Zebrafish embryo Not applicable
  • Chromatiaceae

  • Neisseriaceae

  • (−) Rheinheimera, Pseudomonas, Leptothrix

  • High variability between vehicle control groups in each experiment

  • BPA and BPF caused similar microbial community changes

Catron et al. (2019)
50 µg/kg bw dams dosed orally from GD 15 to weaning Mice Male offspring
  • Bifidobacterium

  • Bacteroidetes

  • BPA acted as an obesogen, induced inflammation, and altered immune responses

  • Supports link between alterations in the gut microbiome and metabolic disease

Malaise et al. (2017)
50 µg/kg bw dams dosed orally from GD 15 to weaning Mice Female offspring Not applicable
  • BPA exposure induced defects in fecal antimicrobial activity and impaired protection of the gut

  • BPA treatment altered the gut-associated immune system and systemic immune response

Malaise et al. (2018)
200 µg/kg bw dams dosed orally from GD 15 to PND 7 Rabbits Male offspring
  • Bacteroidetes

  • Ruminococcaceae

  • Oscillospira (dams)

  • BPA-induced colonic and liver inflammation

  • BPA altered the colonic metabolome

Reddivari et al. (2017)
50 mg/kg feed weight (approximately 10mg/kg bw) F0 dams exposed through chow 2 weeks before mating through PND 30 (weaning), F0 males exposed breeding through weaning Mice Both; yes
  • Mogibacteriaceae, Sutterella spp., and Clostridiales in F0 females

  • ↑ Mollicutes and Prevotellaceae compared in F0 males

  • Bifidobacterium, Mogibacteriaceae in F1 females

  • Akkermansia, Methanobrevibacter in F1 males

  • BPA exposure causes some of the same effects on the gut as ethinylestradiol (EE) exposure and some unique effects compared with EE

  • Clear sex differences in the effects of BPA were evident in both generations

  • BPA-mediated changes in the gut microbiota were inversely related to specific amino acid, lipid, and xenobiotic metabolism/degradation in females

  • BPA-mediated changes in the gut were positively associated with changes in sulfur metabolism, insulin signaling pathway, and steroid hormone biosynthesis in males

Javurek et al. (2016)
Juvenile 30 µg/kg BW gavaged from PND 28 to 56 Nonobese diabetic mice Female
  • ↑ Verrucomicrobia

  • Nitrospira, OD1, AD3, and Gemmatimonadetes

  • Bacterial alterations correlated with blood glucose levels and immune endpoints

Xu et al. (2019
Adult 0, 2, and 20 µg/L and 2 or 20 µg/L BPA + 100 µg/l nano-TiO2 in water environment for 3 months Zebrafish Both; yes
  • ↑ Actinobacteria at 2 µg/L

  • Lawsonia

  • Hyphomicrobium

  • Coexposure to TiO2 antagonized BPA effects at the low dose and synergized at the high dose

  • Similar microbiome effects of BPA in both sexes

  • Serotonin levels in the gut were decreased in BPA-exposed males

  • Changes in gut microbes related to oxidative stress

Chen et al. (2018b)
12–18 µg/kg feed weight in dog food contaminated with BPA can lining, 14 days Dogs, gonadectomized Both; yes but small n
  • Bacteroides spp., Streptophyta, Erysipelotrichaceae, and Flexispira spp

  • Bacteroides ovatus, [Prevotella spp.], [Ruminococcus spp.], and Cetobacterium somerae

  • Exposure to BPA led to an increase in serum BPA levels

  • Some diet by sex interactions observed, but hard to interpret with small sample size

  • Bacteria known to metabolize bisphenols were suppressed with BPA treatment

Koestel et al. (2017)
2000 µg/L in water environment for 5 weeks Zebrafish Male, age not specified BPA altered microbial community; no analysis of statistical significance between groups
  • BPA exposure caused similar changes in the gut as EE

  • Untreated male and female zebrafish have similar gut microbiota

Liu et al. (2017)
In vitro 0–400 µM for 24 h HCT116 human colon cancer cells Not applicable Not applicable
  • BPA treatment decreased cell viability, caused oxidative damage due to ROS accumulation, disrupted mitochondrial function, and promoted apoptosis

Qu et al. (2018)
25, 250, and 2500 µg/L in nutritional medium for 10 days In vitro Simulator of the Human Intestinal Microbial Ecosystem Not applicable
  • BPA ↓ microbial community richness at low doses and increased it at high dose; no analysis of statistical significance between groups

  • Microbacterium and Alcaligenes

  • BPA exposure increased genes related to oxidative stress and altered expression of estrogen receptors

  • BPA is metabolized in the system

Wang et al. (2018b)
0–400 µM for 24 h LS174T human colonic goblet cells Not applicable Not applicable
  • BPA affected the secretory function of intestinal goblet cells by inducing mitochondrial dysfunction, oxidative stress, and apoptosis

Zhao et al. (2018)
Other bisphenols Developmental BPAF (0, 0.2, 0.6, 1.8, 5.2, 15.3, or 45.0 µM), BPB (0, 0.6, 1.7, 5.1, 15.0, or 44.0 µM), BPF (0, 0.2, 0.6, 1.8, 5.2, 15.3, 45.0 µM), BPS (0, 0.2, 0.6, 1.8, 5.2, 15.3, 45.0 µM) in water environment for 10 days Zebrafish embryo Not applicable
  • Neisseriaceae (BPS)

  • Cryomorphaceae (BPS)

  • Chromatiaceae (BPF)

  • Neisseriaceae (BPF)

  • Exposure to the least developmentally toxic bisphenols impacted microbiota the most (BPS, BPA, BPF); the most developmentally toxic bisphenols did not impact microbiota (BPB, BPAF)

  • Similar microbial changes for BPA and BPF exposure, unique profile for BPS exposure

  • High variability between vehicle control groups in each experiment

Catron et al. (2019)