Anti-Vitellogenin monoclonal antibody, clone PF-5E5

Alligator gar populations have declined because of overfishing, habitat loss and pollution. Over time, the exposure to different pollutants have affected these fishes as a consequence of their high trophic level, bottom-dwelling habits and long life span. In order to evaluate the physiological effects of pollutants on alligator gar, juveniles (6, 12 and 24 months) were exposed to sub-lethal doses of diazinon, beta-naphthoflavone (BNF) and 17 beta-estradiol (E2) by intraperitoneal injection. After 2 days of exposure, liver samples were taken to determine the activities of acetylcholinesterase, butyrylcholinesterase and carboxylesterase; alkaline and acid phosphatases (ALP and ACP); ethoxyresorufin o-deethylase (EROD); glutathione s-transferase (GST); superoxide dismutase (SOD), and vitellogenin (VTG) concentration. Two additional bioassays consisting on the exposure of compounds through water or food were performed and after 4 and 28 days, respectively, biomarkers were determined. All esterases were inhibited in organisms exposed to diazinon as well as in 6-months gar exposed to E2 and BNF. In contrast, ALP activity increased in gar exposed to diazinon and E2, while ACP activity did not show any variations. No EROD activity was registered after exposure to the different pollutants, despite being one of the most sensitive and common detoxification biomarkers used for fishes. GST activity reduction was detected when gar were exposed to E2 and BNF, while SOD activity increased after exposure to diazinon and E2. Finally, VTG levels were higher in animals exposed to E2 compared to other treatments. Overall, these results suggest that alligator gar juveniles have a low biotransformation metabolism and show that they are especially sensitive to those pollutants affecting the nervous system.

As a potential endocrine disruptor, tris(2,3-dibromopropyl) isocyanurate (TBC) has previously been demonstrated to reduce expression of estrogen-dependent vitellogenin (vtg) mRNA in adult zebrafish. However, the underlying toxicity pathways and molecular mechanisms involved in TBC-induced endocrine disruption remain elusive. In the current study, E-Screen and MVLN assays were employed to explore the potential anti-estrogenic effects of TBC via the estrogen receptor alpha (ER alpha)-mediated signaling pathway. Within a dose range between 1 x 10(-9) and 1 x 10(-7) M, TBC significantly inhibited 17 beta-estradiol (E-2)-induced cell proliferation in a breast cancer cell line. The luciferase activity induced by E-2 was also significantly inhibited by TBC in a dose-dependent manner. Moreover, neither TBC nor E-2 affected proliferation of the ER alpha-negative breast cancer cell line MDA-MB-231. These experimental results confirmed that TBC has anti-estrogenic effects by affecting the ER alpha-mediated signaling pathway. By comparing TBC with known antagonists of ER alpha, we found that TBC has similar molecular structure as certain co-activator binding inhibitors. Therefore, using molecular docking and molecular dynamics simulations, TBC was further predicted to competitively occupy the surface site of ER alpha rather than the canonical E-2-binding pocket of ER alpha, thus disrupt subsequent co-activator recruitment and transcription activation. Our findings elucidate the anti-estrogenic mechanism of TBC at the atomic level and highlight the biological importance of surface sites of nuclear receptors for a risk assessment of potential environmental pollutants.