Kidney effects drove the EU safety review
A two-year rat feeding study found that female rats at all tested doses showed increased kidney calcification and pelvic epithelial changes. EFSA's 2010 panel concluded the dose previously treated as a no-adverse-effect level should actually be classified as a low observed-adverse-effect level, which is why the acceptable daily intake was cut to roughly a third of the previous figure. The findings were in animals at doses well above likely human intake from food use.
A 2-year rat study found renal calcification and pelvic epithelial hyperplasia with degenerative changes in females at all dose levels tested. EFSA reclassified the prior no-adverse-effect level as a low observed-adverse-effect level, leading to a lower ADI.
2010AnimalEFSA Scientific Opinion on the re-evaluation of Amaranth (E 123) as a food additive, EFSA Journal 2010;8(7):1649
EFSA established an ADI of 0.15 mg/kg body weight per day, significantly lower than the previous Scientific Committee on Food figure of 0.8 mg/kg bw/day and the JECFA figure of 0.5 mg/kg bw/day.
2010Regulatory reviewEFSA Scientific Opinion on the re-evaluation of Amaranth (E 123) as a food additive, EFSA Journal 2010;8(7):1649
Reproductive and developmental toxicity signals
Several studies in mice, rats, rabbits, cats and dogs contributed to setting the acceptable daily intake. Although the panel noted methodological weaknesses in some studies, they were collectively considered sufficient to establish no-adverse-effect levels across multiple species. These findings, taken together with the kidney data, defined the safety threshold that regulators now use.
Reproductive and developmental toxicity studies across multiple species (mouse, rat, rabbit, cat, dog) contributed to setting the ADI alongside the 2-year kidney study. The combined dataset shifted the point of departure to 15 mg/kg bw/day.
2010AnimalEFSA Scientific Opinion on the re-evaluation of Amaranth (E 123) as a food additive, EFSA Journal 2010;8(7):1649
Carcinogenicity: US ban versus EU assessment
The FDA banned Amaranth in 1976 after a Soviet study reported tumour formation in rats and the FDA's own tests were inconclusive. Under the Delaney clause, which prohibited chemicals where cancer risk could not be ruled out, the FDA delisted it. EFSA's 2010 re-evaluation reviewed all available data and concluded Amaranth is neither genotoxic nor carcinogenic. The US ban reflects a 1970s regulatory standard rather than a finding of proven human carcinogenicity.
The FDA terminated certification of FD&C Red No. 2 in February 1976 after inconclusive tests on carcinogenicity in female rats at high doses, applying the Delaney anticancer clause which prohibited use when cancer risk could not be excluded.
1976RegulatoryUS Federal Register announcements, February 1976; FDA CPG Sec 587.200
EFSA's ANS Panel concluded that Amaranth is not genotoxic and not carcinogenic based on review of all available toxicological data.
2010Regulatory reviewEFSA Scientific Opinion on the re-evaluation of Amaranth (E 123) as a food additive, EFSA Journal 2010;8(7):1649
Gut breakdown and aromatic amine metabolites
Azo dyes including Amaranth are broken down by gut bacteria into aromatic amine compounds. Research shows Amaranth is reduced by more bacterial species than other common azo food dyes. The toxicological significance of its specific metabolites in humans at food-use doses has not been fully characterised. This is a general concern for the azo dye class, and Amaranth's gut metabolism received less individual study than some other members of the group.
Among four food azo dyes tested, Amaranth was reduced by the highest number of bacterial species in the human gut microbiome, releasing aromatic amine metabolites via reductive cleavage of the azo bond.
2023LabMetabolism of azo food dyes by bacterial members of the human gut microbiome, ScienceDirect (Food and Chemical Toxicology), 2023
Azo dye metabolites produced by intestinal microorganisms include compounds with potential toxicological activity. The review notes that parent dyes classified as acceptable may generate different breakdown products in the human gut environment.
2018LabToxicological significance of azo dye metabolism by human intestinal microbiota, PMC5870118
Heavy aperitif drinkers may exceed the ADI
EFSA's 2013 refined exposure assessment found that the average person consuming food and drinks containing Amaranth at permitted levels stays well within the ADI. However, adults who regularly drink large amounts of vermouth-based aperitifs and aromatised wines at the maximum permitted colour concentration could exceed the ADI by around six times. Children's exposure from permitted products was estimated to be about 30 times below the ADI.
Adults who regularly consume high amounts of Americano cocktails and aperitif wines containing Amaranth at maximum permitted levels could exceed the ADI approximately 6-fold. Mean adult exposure from all sources remained below the ADI.
2013Regulatory reviewEFSA Refined exposure assessment for Amaranth (E 123), EFSA Journal 2013;11(10):3442
Allergic reactions in sensitive individuals
As with other azo dyes, Amaranth can trigger reactions in people who are sensitive to azo compounds, particularly those with aspirin intolerance or asthma. Reported reactions include urticaria (hives), skin rash, and in some cases worsening of asthma symptoms. The number of documented cases in the literature is small, and this cross-reactivity is a recognised class property of azo dyes rather than unique to Amaranth.
Azo dye sensitivity, including reactions to Amaranth, can manifest as urticaria, angioedema, and asthma-like symptoms, particularly in individuals with aspirin intolerance. Only a limited number of intolerance reactions to Amaranth specifically have been reported.
ObservationalMultiple secondary sources citing case reports; general azo dye sensitivity literature