ACESULFAME POTASSIUM* Explanation Acesulfame K was evaluated by the Joint FAO/WHO Expert Committee on Food Additives in 1981 (see Annex I, Ref. 57). Some shortcomings were apparent in the long-term/carcinogenicity studies in the mouse and rat and no ADI for man was allocated. A toxicological monograph was prepared (see Annex I, Ref. 58). Since that evaluation, additional studies have become available and are summarized and discussed in the following monograph addendum. BIOLOGICAL DATA BIOCHEMICAL ASPECTS Absorption, distribution and excretion Single oral doses of approximately 15 mg 14C-acesulfame K/kg bw were administered to male and female rats which had been pretreated with unlabelled Acesulfame K at a level of 300 mg/kg diet for 60 days. Control animals without pretreatment were also similarly dosed with 14C-acesulfame K. In all animals 95.1-98.2% of the dose was recovered in urine and cage washings, and 0.95-2.86% in faeces. Total recoveries were 96.3-99.2%. Excretion of radioactivity was rapid, 92.6-96.8% of the dose being excreted within 24 hours and displayed biphasic kinetics. The half-life of the rapid phase was 4-4.5 hours and for the slower phase (accounting for <0.5% of the dose) was 109-257 hours. No significant differences in route or rate of excretion were observed between sexes nor between controls and animals pretreated with Acesulfame K for 60 days (Volz & Eckert, 1981). Biotransformation Separation by TLC of urinary extracts from rats used in the above study revealed only one peak which was identical with Acesulfame K. No metabolites were detected in control or Acesulfame K-pretreated animals (Volz & Eckert, 1981). * Monograph addendum. TOXICOLOGICAL STUDIES Special studies on DNA binding After pretreatment for seven days with a diet containing 3% Acesulfame K, male rats were given a dose of 250 mg Acesulfame K containing 14C-acesulfame K (9.6 x 108 dpm) by oral gavage. After eight hours the animals were killed and liver and spleen excised; DNA and chromatin protein was isolated from these organs. No radioactivity could be detected on any DNA sample. A low level of activity (8-11 dpm/mg protein) was associated with chromatin protein and this was claimed to be due to non-covalent interactions of unchanged Acesulfame K (Sagelsdorff et al., 1981). Special studies on nitrosation of Acesulfame K Acesulfame K was incubated at 37°C with excess NaNO2 (276 mg/100 ml) at pH 3 and pH 1 for one hour and four hours. The maximum yield of N-nitroso derivative was 1.4 x 10-3% after four hours at pH 1. This was considered to represent a negligible hazard in vivo (Eisenbrand, 1982). Special studies on the possible reactions of Acesulfame K with food constituents Acesulfame K (1% aqueous solutions) was heated at 100°C with the model food constituents, ethanol, sorbitol, glycine, alanine, glutamic acid, phenyl alanine or n-butylamine, in acetate buffer at pH 5. Analysis by HPLC and UV-spectrometry failed to detect any decomposition or interaction products of Acesulfame K in any of the model systems (Clauss, 1981). Long-term studies Rat In the previous evaluation, it was observed that some shortcomings were apparent in the second long-term feeding study in rats, in that only a small proportion of the animals in the control and top-dose (3% Acesulfame K) groups were examined histopatho- logically in detail. A detailed histopathological examination has now been performed on the remaining animals in the control and top-dose groups, and on all animals in the lower (0.3% and 1%) dose groups. It was concluded that there were no treatment-related histopathological changes and, in particular, no evidence of an increase in the incidence or alteration of the biological type of the neoplasms diagnosed (Newman, 1982). Comments The absence of mutagenic activity in several in vitro and in vivo assays together with negative results in the two-year study in rats indicate that Acesulfame K is devoid of mutagenic/carcinogenic activity. The earlier mouse carcinogenicity study, though not meeting current requirements, was also negative. EVALUATION Level causing no toxicological effect Rat: 3% (30 000 ppm) in the diet, equal to 3-1.5 g/kg bw. Dog: 3% (30 000 ppm) in the diet, equal to 900 mg/kg bw. Estimate of acceptable daily intake for man 0-9 mg/kg bw. REFERENCES Clauss (1981) Model experiments aimed at detecting possible reactions of Acesulfame K with constituents of food. Unpublished report submitted to WHO by Hoechst A.G. Eisenbrand, G. (1982) The nitrosatability of Acesulfame potassium in the nitrosamine assay procedure of WHO. Unpublished report submitted to WHO by Hoechst A.G. Newman, A. J. (1982) Pathology report of the combined chronic toxicity and carcinogenicity study with Acesulfame K in rats. Unpublished report submitted to WHO by Hoechst A.G. Sagelsdorff, P., Lutz, W. K, & Schlatter, Ch. (1981) Research Report No. 40182A. Unpublished report submitted to WHO by Hoechst A.G. Volz, M. & Eckert (1981) Research Report No. 01-L42-0352-81. Unpublished report submitted to WHO by Hoechst A.G.
See Also: Toxicological Abbreviations Acesulfame Potassium (WHO Food Additives Series 16) Acesulfame potassium (WHO Food Additives Series 28) ACESULFAME POTASSIUM (JECFA Evaluation)