Tartrazine (TTZ) is an azo dye used as a colorant in food products, drugs, and cosmetics. The present study evaluates the impacts of TTZ on embryonic development of zebrafish ( Danio rerio). Laboratory-raised D. rerio embryos (n = 20/concentration) were exposed to graded dilutions of TTZ (0, 0.1, 1, 2, 3, 4, 5, 10, 20, 30, 40, 50, 75, and 100 mM) from gastrulation stage (5.25 hours postfertilization [hpf]) until hatching and developmental trajectory was traced up to day 7. The no observed effect concentration (NOEC), median lethal concentration (LC), median effective concentration (EC), and teratogenic index (TI) were calculated. Exposure of embryos to < 10 mM TTZ had no effects; 20 to 30 mM TTZ caused tail bending, cardiac and yolk sac edema in 50% of larvae; in 30 to 50 mM TTZ-exposed embryos the heart rates declined along with the above mentioned deformities, causing mortality within 96 to 144 hpf; development ceased completely at 75 to 100 mM concentration. The NOEC and LC were recorded at 5 and 29.4 mM dose, respectively. The EC values for heart rate, cardiac edema, tail bending, and hatching success were at 59.60, 53.81, 98.28, and 58.97 mM with TI quotient 0.49, 0.54, 0.29, and 0.49, respectively. We conclude that TTZ is not embryo toxic/teratogenic for zebrafish embryos up to a dose level of 10 mM concentration.

In this study, we tested the teratogenic/embryotoxic potentials of food colorant, Sunset Yellow (E110) using zebrafish embryos as a model. Laboratory‐raised developing embryos of Danio rerio were exposed to graded concentrations (00, 0.1, 1.0, 2.0, 3.0, 4.0, 5.0, 10, 20, 30, 40, 50 and 100 mm) of E110 from gastrulation stage (~6 hours post‐fertilization [hpf]) up until hatching. The developmental trajectory of each embryo and post‐hatched larva was traced from 24 to 168 hpf. The no observed effect concentration (NOEC), median effective concentration (EC50), median lethal concentration (LC50) and teratogenic index were determined. In the 0.1 mm E110‐exposed embryos, the development proceeded as in controls (NOEC), while, exposure of embryos to 1‐5 mm of E110 led to a decrease in body size, dry body mass of resultant larvae along with appearance of morphological deformities such as, microphthalmia, pericardial edema, yolk sac edema and spinal curvature. Larvae of 10‐50 mm E110‐exposed embryos exhibited increased cellular apoptosis in the cardiac region with significantly declined heartbeats and elevated mortality rates, in addition to the above‐mentioned abnormalities. In the 100 mm exposure group, all embryos succumbed to death within 24 hpf. The NOEC and LC50 recorded were at 0.1 and 42.57 mm respectively. EC50 (96 hpf) recorded for pericardial edema and yolk sac edema was 19.41 and 39.84 mm with teratogenic index quotient 2.1 and 1.06 respectively The study provides direct evidence for the developmental toxicity/teratogenic potential of E110.

No abstract