Morbidity/mortality following developmental exposure to BPA (A,B), E2 (C), or GSK4716 (D). (A) Percentage of chorion intact (dotted black line) versus chorion removed (solid grey line) larvae exhibiting abnormalities following static waterborne exposure to BPA (10 – 100 μM). Statistical significance determined by unpaired T-test for each concentration (p<0.05). Error bars depict SEM. (B-D) Percentage of larvae exhibiting abnormalities (grey circles) or percent mortality (black squares) following static waterborne exposure to BPA (10 – 70 μM; note: data points (x-axis) are plotted at the actual exposure concentrations, which were adjusted following quantification of stock concentration and were slightly higher than expected; e.g., “20 μM” exposure was actually 24.46 μM) (B), E2 (0.1 – 25 μM) (C), or GSK4716 (0.1 – 30 μM) (D) from 8-120 hpf. Plot shows % affected versus log(exposure concentration) ±SEM (BPA: N=6, 12 embryos per group; E2 and GSK4716: N=5, 8 embryos per group). Curves were fit by a nonlinear regression dose-response analysis. Note: controls for BPA were 12.8% (abnormality) and 0% (mortality); controls for E2 and GSK4716 were 2.5% (abnormality) and 0% (mortality). Statistical significance determined by one-way ANOVA on ranks (Kruskal-Wallis), Student-Newman-Keuls post-test compared to vehicle-exposed embryos, *p<0.05. Error bars depict SEM. (E) Representative photos of 5 dpf larvae showing physical effects of BPA, E2, or GSK4716 exposure. Numbers depict exposure concentrations (μM). Most common observed effects were yolk sac edema, pericardial edema, craniofacial abnormalities, or axis defects.