QUINOLINE YELLOW* Explanation Quinoline Yellow was previously evaluated by the Joint FAO/WHO Expert Committee on Food Additives in 1966, 1969, 1974, 1975, 1978, and 1982 (Annex I, Refs. 13, 19, 35, 36, 38, 39, 46, 47, 48, 50, and 60). As the last evaluation, the temporary ADI of 0-0.5 mg/kg body weight was extended to 1984 pending the results of metabolism studies and a long-term toxicological study which were in progress. The committee noted that there are two quinoline yellows, one of which is about 30% methylated and the other non-methylated, and considered that data from both compounds could be used for toxicological evaluation of either of the quinoline yellows for food additive use. Since the previous evaluation, additional data has become available and is summarized and discussed in the following monograph addendum. BIOLOGICAL DATA BIOCHEMICAL ASPECTS Absorption, distribution and excretion After administration of a single intra-gastric dose of 4 mg 14C- Quinoline Yellow to male Sprague-Dawley rats, only about 2% of the radioactivity was eliminated in the urine and 94% was recovered in the faeces within 120 hours. At termination, approximately 0.14% of the activity remained in the carcass and negligible amounts were found in expired air. Groups of 4 (2 males, 2 females) Sprague-Dawley rats were given a single intra-gastric dose of 1 mg/kg body weight 14C-Quinoline Yellow and blood levels of radioactivity were measured at intervals of 1/4, 1/2, 1, 2, 4, 8, 24 and 48 hours after treatment. The peak of radioactivity appeared in the total blood and the plasma between 0.5 and 1 hour after dosing. All the radioactivity was found in the plasma and did not appear to enter the erythrocytes. The maximum plasma concentration was less than 0.009% of the dose and most the activity was bound to plasma proteins; the unbound, ultrafilterable activity was 4% of the total plasma activity after 4 hours and 10% after 8 hours. The kinetics of the blood levels fitted a two-compartment model with the following parameters: Tal/2 = 0.6 hour; Tll/2 = 11.8 hours and T21/2 ; 70.0 hours. * Monograph addendum Biliary excretion studies were performed in rats dosed with 14C-Quinoline Yellow (2.85 mg/kg body weight) by gastric intubation. The peak of biliary excretion occurred between 1.5 hour and 3 hours after dosing and about 1% of the dose was excreted by this route in 31.5 hours. Whole body autoradiography of male rats given a single oral dose of 14C-Quinoline Yellow demonstrated that, after 1 hour, the activity was primarily associated with the gastro-intestinal tract and excretory organs; after 24 hours only the large intestine and, to a minor degree, the cortical zone of the kidney displayed activity. Tissue distribution studies were performed in female rats after intra-gastric administration of 14C-Quinoline Yellow; single animals were sacrificed after 1/2, 1, 4, 8, 24 and 48 hours and radioactivity measured in the stomach, small intestine, caecum, large intestine, liver, kidney, bladder, brain, muscle, ovary, lung, pancreas, splen, thyroid, blood and carcass. The results indicated that only a small proportion of the dose was absorbed from the gastro-intestinal tract and this was primarily associated with the liver, kidney and bladder. The maximum proportion of the dose found in these organs was: liver, 0.4% after 4 hours; ca 1.0% after 8 hours; bladder ca 0.02% after 8 hours. When the results were expressed as concentration factors (radioactivity/g tissue) there appeared to be a selective concentration of activity in the thyroid which persisted up to 48 hours; a relatively high concentration was found in the ovaries in the first 24 hours but not after 48 hours. The total amount of activity absorbed from the gastro-intestinal tract was estimated to be 3 to 4% of the administered dose (Anon, 1978). In a complementary study carcasses of male rats which had been used to determine blood levels of activity in the studies described above were dissected and residual tissue levels determined corresponding to 1/2, 1, 4, 8, 24 and 48 hours after dosing. Similarly, activity was measured in the tissues of male rats used in the excretion balance studies 120 hours after dosing. The results confirmed that activity was selectively concentrated in the thyroid (Anon, 1978). Studies of blood levels and excretion of 14C-Quinoline Yellow were performed in beagle dogs after intravenous or intragastric administration. After i.v. administration of 0.2 mg 14C-Quinoline Yellow/kg body weight, the disappearance of radioactivity corresponded to a two-compartment pharmaco-kinetic model with elimination coefficients of 0.1971h-1 and 0.0163h-1. Following intra-gastric administration of 0.44 mg 14C-Quinoline Yellow/kg body weight the peak blood levels were observed after between 1 and 4 hours. Approximately 22% of an i.v. dose of 14C-Quinoline Yellow was excreted in the faeces in this period. After intra-gastric dosing, 1-4% of the label appeared in the 0-72 hours urine, mainly between 8 and 48 hours, and 42-60% was excreted in faeces within 72 hours. Residual tissue levels after 72 hours were low and did not indicate any specific tissue accumulation, particularly in the thyroid (Anon, 1978). Metabolism Chromatographic examination of bile, urine, faeces and plasma of rats given intra-gastric doses of 14C-Quinoline Yellow indicated that the colour was metabolised to only a small extent. In the urine, between 10 and 15% of the activity was associated with an unidentified metabolite which was more polar than the unchanged colour. Similar experiments in beagle dogs, in which urine, faeces and plasma were examined, indicated that Quinoline Yellow is metabolised to only a small extent in this species. TOXICOLOGICAL STUDIES Long-term studies A long-term chronic toxicity/carcinogenicity study was carried out in the OFI mouse following in utero exposure. Four groups of mice, containing 105 animals of each sex in the control and 65 of each sex in the treatment groups, were fed diets 0, 0.1%, 0.3% and 1.0% Quinoline Yellow in the diet from age 4-5 for a 9 week period prior to mating (Fo generation). The animals were then mated monogamously with partners from the same treatment groups and the females maintained on their respective experimental diets throughout gestation and lactation. The number of live and still-born pups was recorded and the litter size reduced to 8 on the third day after parturition. On day 21 after parturition, animals were selected from the litters of the appropriate treatment groups to provide groups of 100 animals of each sex (controls) or 50 animals of each sex (test groups). These animals comprising the F1 generation were housed singly and maintained on their respective diets for 21 months in the case of males, and 23 months in the case of females. Body weight and food intake were measured weekly for the first 3 months, twice a months from 3 to 6 months and monthly thereafter. Haematological examinations were performed after 3, 6, 23 and 18 months of treatment and at termination of the study. All animals dying or moribund animals sacrificed during the study and those at terminal sacrifice were autopsied and abnormal tissues were samples for histological examination. In addition, a histological examination was carried out on all the animals from the control and top dose groups at termination. The organs examined histologically were: liver, gall bladder, kidneys, heart, lungs, brain (cerebrum), gonads, seminal vesicles, epididymis/uterus, prostate/ vagina, salivary gland, peripheral nerve, adrenal, pituitary, Harderian gland, oesophaagus, stomach, duodenum, nose, spleen, jejunum, ileum, caecum, colon, urinary bladder, trachea, vena cava, aorta, pancres, thymus, skin, mammary gland, skeletal muscle, optic nerve, femur, eyes, thyroid, lymph nodes, spinal column. Organ weights were recorded of: brain, heart, liver, spleen, kidneys, gonads, stomach, jejunum, caecum (full and empty). The growth rats and mortality rates during the course of the study showed no significant dose-related effects; the mortality rates at termination were, for males and females respectively, 60% and 71% in controls, 50% and 72% in the 0.1% groups, 54% and 58% in the 0.3% group and 68% and 68% in the 1% dose group. The number of animals bearing palpable masses remained low (about 20%) and the incidence and time of onset was similar in all groups. On comparing the top dose animals with controls at termination, there was no important difference in the tumour types observed nor in the overall incidence of tumours. Systematic histological examination of all the tissues samples in the top dose group and controls at termination and of any abnormal tissue or rumour observed in all groups showed no treatment-related toxic effects (Coquet et al., 1981). Comments Quinoline Yellow is absorbed from the gastro-intestinal tract to only a small extent in rats and dogs, and most of an orally administered dose is excreted unchanged. No adverse effects of treatment were seen in the two-generation long-term study in mice. In particular there was no observed effect on thyroid function or histopathology and no evidence of carcinogenicity. EVALUATION Level causing no toxicological effects Mouse: 1% of the diet, equal to 1.500 mg/kg/ Estimate of an acceptable daily intake for man 0-10 mg/kg bw. REFERENCES ANON (1978) Etude de la distribution chez le rat du jaune de quinoleine ou E104 marqué au 14C. Unpublished report of the Laboratoire d'Etudes du Métabolisme des Médicaments (Laboratory for the Study of Drug Metabolism), Commissariat à l'Energie Atomique, France. COQUET, B., RONDOT, G., NEWMAN, A.J., GENOUX, P., JAHCHAN, A., MARY, M.C., & BLANC, J.P. (1981) Carcinogenicity study in the OFI Mouse with Colouring Agent E104 Quinoline Yellow. IFREB Report No. 110202 - October 2, 1981. Unpublished Report of the EEC Colours Group.
See Also: Toxicological Abbreviations Quinoline yellow (FAO Nutrition Meetings Report Series 46a) Quinoline yellow (WHO Food Additives Series 6) Quinoline Yellow (WHO Food Additives Series 8) Quinoline yellow (WHO Food Additives Series 13) QUINOLINE YELLOW (JECFA Evaluation)