Table 1.
References | Compound | Dose Exposure | Justification of Exposure Dose | Species Strain Mode | Methods | Outcomes | Conclusions |
---|---|---|---|---|---|---|---|
Van de Wiele et al. (2010) [35] | Metal (Arsenic) | 10 μg methylarsenical/g biomass/hr and 28 μg as-contaminated soils/g biomass/hr | Concentrations detected in arsenic contaminated soils in urban areas of the EEUU | Strains isolated from human feces | HPLC; plasma mass spectrometry | High degree of methylation of Methylarsenical and As-contaminated soils in colon digestion. | Human microbiota has ability to actively metabolize As into methylated arsenicals and thioarsenicals. |
Wang et al. (2018) [28] | BPA | 25 μg/L, 250 μg/L, and 2500 μg/L | High human relevant exposure dose; EPA reference dose; 1% lowest observed adverse effect level | Humans | In vitro SHIME, 16S rRNA gene sequencing, and PCR | BPA exposure decreased the diversity of gut microbioma (ascending colon and the transverse colon). Exposure to BPA of 25 μg/L decreased diversity of gut microbioma, but high-level exposures (250 and 2500 μg/L) increased diversity (descending colon). | Exposure to BPA significantly altered the microbiota and increased the proportion of shared microbes. |
Hoffman et al. (2019) [36] | PCB126 | 20 or 200 μM | Concentrations physiologically relevant, especially in heavily exposed populations | C56BL6/J mice | 16S rRNA gene sequencing, PCR, and HPLC | Significant reduction in bacterial growth after exposure to high concentrations of PCB 126 compared to control. Not significant reduction in bacterial growth at PCB concentrations below 20 µM. | Exposure to PCB126 can contribute to alterations in host metabolism through mechanisms dependent on the intestinal microbiota, specifically through bacterial fermentation or membrane disruption. |
Lei et al. (2019) [37] | Di (2-ethylhexyl) phthalate | 10 or 100 µM | The concentration mimics human exposure during adolescence by continually exposing mice to phthalate from ages 6 to 8 weeks | C57BL/6J mice | 16S rRNA gene sequencing and a triple-quadrupole time-of-flight instrument coupled to a binary pump HPLC system | Exposure of in vitro cecal microbiota to di (2-ethylhexyl)-phthalate increased the abundance of Alistipes, Paenibacillus, and Lachnoclostridium. Non-directed metabolomics showed that di (2-ethylhexyl)-phthalate greatly altered the metabolite profile in the culture. | Di (2-ethylhexyl)-phthalate can directly affect the production of bacterial metabolites related to neurodevelopmental disorders. |
Joly et al. (2013) [38] | Chlorpyrifos | 1 mg/kg/day | NOAEL | Wistar rats | SHIME | Exposure to chlorpyrifos increased Bacteroides spp. and Enterococcus spp. and reduced Bifidobacterium spp. and Lactobacillus spp. | Chronic, low-dose exposure to chlorpyrifos causes gut dysbiosis. |
Shehata et al. (2013) [39] | Glyphosate | 5.0, 2.40, 1.20, 0.60, 0.30, 0.15, and 0.075 mg/mL | To determine the minimal inhibitory concentration | Chickens | MALDI–TOF MS analysis, multiplex PCR | In vitro exposure to glyphosate showed resistance to glyphosate in highly pathogenic bacteria, but most beneficial bacteria showed susceptibility to glyphosate. | Glyphosate exposure showed differences in sensitivity between pathogenic and beneficial microbiota. Ingestion of glyphosate-contaminated food reduced the beneficial microbiota. |
Ackermann et al. (2015) [40] | Glyphosate | 0, 1, 10, and 100 μg/mL | Concentrations lower than NOAEL | Cows | DAISYII-incubators, FISH with 16S rRNA/23S rRNA-targeted | Exposure to 1 and 10 μg/mL glyphosate reduced abundances of all species except for Isotricha spp. and Diplodinium spp. Exposure to 100 μg/mL glyphosate reduced abundance of Diplodinium spp. | Glyphosate inhibits growth of beneficial bacteria, but increases the population of pathogenic bacteria |
Riede et al. (2016) [41] | Glyphosate | 0.42 or 2.92 mg/L | The low dose reflects the estimated maximum dietary glyphosate intake of dairy cattle, according to model assumptions. The high dose is higher than residues found in the beef cattle diet. | Cows | RUSITEC experiments, LC-MS/MS method, 16S rRNA gene sequencing, and PCR | Effects of glyphosate at concentrations of 0.42 or 2.92 mg/L. After the incubation period only observed subtle changes in the composition of ruminal bacteria. | No major changes were observed due to Glyphosate exposure to ruminal metabolism or the composition of bacterial communities. |
HPLC: high performance liquid chromatography; PCR: polymerase chain reaction; SHIME: simulator of the human intestinal microbial ecosystem; FISH: fluorescence in situ hybridation; MALDI-TOF MS: matrix-assisted laser desorption/ionization time-of-flight mass spectrometry; RUSITEC: rumen simulation technique; NOAEL: no observed adverse effects level.