Table 2.
Model System(in vivo) | Chemical | Source/Use | Proposed Mechanism | Effects | References |
---|---|---|---|---|---|
Mice | Tributyltin (TBT) | Biocide/antifoulant/pesticide | PPARγ and RXRα agonist | Increases epididymal adipose mass in adults. Increases lipid accumulation in adipose depots, liver, and testis of neonate mice. | (49) |
Bisphenol A (BPA) | Found in plastic products such as water pipes and toys; found in electronic equipment | Acts partially through GR signaling; enhances expression of adipogenic genes and lipogenic enzymes, acts on PPARγ | Increases body weight, fat mass, chronic inflammation, and inflammation in white adipose tissues. | (71, 72) | |
Bisphenol S (BPS) | A BPA substitute; used in the manufacture of plastics and resins. Ingestion from food is the major source of BPS exposure | PPARγ activator; increases expression of PPARγ | Increases liver triglycerides, causes hyperinsulinemia, induces changes in gene expression, causes changes in liver DNA methylation. |
(73, 74) | |
Diethylstilbestrol (DES) | A synthetic estrogen previously used in pharmaceuticals during pregnancy | Estrogenic activity | Induces significant increase in body weight and reproductive abnormalities | (75, 76) | |
Dichlorodiphenyltrichloroethane (DDT) and dichlorodiphenyldichloroethylene (DDE) | Pesticide DDE is the metabolite of DDT |
Inconclusive | Induces thermogenic impairment of brown adipose tissue, obesity, insulin resistance, and dyslipidemia | (77, 78) | |
DBT | Used to make of polyvinyl chloride (PVC) plastics and medical devices | PPARγ and RXRα agonist; increases the expression of adipogenic genes | Induces increased lipid accumulation, fat storage, leptin levels, and glucose intolerance. | (79) | |
Triflumizole | Fungicide | PPARγ activator |
Increases adipose depot weight and adipogenic gene expression | (80) | |
Tolylfluanid | Fungicide | Acts through glucocorticoid receptor signaling | Induces higher body weight, fat mass, visceral adipose depots, glucose intolerance, insulin resistance, and metabolic and energy disturbances | (81) | |
Diethyl-hexyl-phthalate (DEHP) | Found in personal care products, lubricants, pesticides, paints, and PVC plastics. Exposure is mainly through food via food packaging | PPARγ activator | Increases body weight, adipose tissue, lipids, and glucose levels | (82) | |
Cadmium (Cd) | Ingestion of contaminated foods | Inconclusive | Induces metabolic syndrome-like phenotypes (impaired glucose and insulin functioning, hepatic steatosis, weight gain, increase in fat), oxidative stress and mitochondrial dysfunction. | (83) | |
Di (2-ethylhexyl) phthalate | Used in the making of PVC plastics and vinyl products; used in lubricants, emulsifying agents, and cosmetics | Possible PPARγ activator | Induces glucose intolerance, insulin resistance, hepatic steatosis/steatohepatitis, increased leptin levels, increased cholesterol, and white adipose tissue disfunction. | (84) | |
Rats | Bisphenol A (BPA) | Found in plastic products | Activates Erα and Erβ; thyroid hormone receptor antagonist | Induces an increase in body weight and white adipose tissue, adipocyte hypertrophy, and increased expression of adipogenic genes | (85) |
Tributyltin (TBT) | Biocide and molluscicide | RXR and PPARγ activation | Causes ovarian obesogenic effects | (86) | |
Zebrafish (Danio rerio | Mono ethyl phthalate (MEHP) and | Primary metabolite of di(2-ethylhexyl) phthalate (DEHP) |
PPARγ agonist | Obesogenic properties | (87) |
Tetrabromobisphenol A (TBBPA) | Flame retardant | PPARγ agonist | Obesogenic properties | (87) | |
Cadmium | Ingestion of contaminated foods, cigarette smoke, and breathing contaminated air | Inconclusive | Increased lipid accumulation | (88) | |
Frog (Xenopus laevi) | Tributyltin (TBT) | Biocides, antifoulants, pesticides | PPARγ and RXRα agonist | Formation of ectopic adipocytes in and around gonadal tissues | (49) |