IPCS INCHEM Home

    METHYL ANTHRANILATE

    Explanation

         Methyl anthranilate was reviewed at the eleventh meeting of the
    Joint FAO/WHO Expert Committee on Food Additives, specifications were
    prepared, and a conditional acceptable daily intake for man (ADI) of
    0-1.5 mg/kg bw was established (FAO/WHO, 1967; FAO/WHO, 1968).

         Since this previous review, new data has become available and is
    included in this monograph.

    BIOLOGICAL DATA

    BIOCHEMICAL ASPECTS

         Substantial evidence has accumulated showing that many esters
    readily undergo enzymatic hydrolysis into their component alcohols and
    acids (F.E.M.A., 1974; Longland et al., 1977; Grundschober, 1977). In
    the case of methyl anthranilate, there is direct experimental evidence
    showing that this ester, while only slowly hydrolysed by artificial
    gastric or pancreatic juice, was readily hydrolysed in rat liver
    homogenate (50% in 26.6 minutes) and rapidly hydrolysed in a
    homogenate of rat small intestine mucosa (50% in 2.5 minutes)
    (Longland et al., 1977). Methyl anthranilate has also been shown to be
    completely hydrolysed (>99% in two hours) in pig liver homogenate;
    but was more resistant to hydrolysis in pig jejunum homogenate and
    completely unhydrolysed by a pancreatin preparation (Grundschober,
    1977).

         The hydrolysis products of methyl anthranilate are, of course,
    methyl alcohol and anthranilic acid. Methyl alcohol is readily
    metabolized via well-known pathways to carbon dioxide and water
    (Williams, 1959; Harger, 1967). Anthranilic acid is a normal
    metabolite in man and is excreted in the urine, primarily, as
    o-aminohippuric acid and to a lesser extent as anthranilic acid
    glucuronide. Data are also available on other species (rat, rabbit,
    cat, dog) (Charconnet-Harding et al., 1953; Price et al., 1956; Brown
    & Price, 1956; Williams, 1959).

    TOXICOLOGICAL STUDIES

    Special studies on carcinogenicity

         There was no increase in the incidence of primary lung tumours in
    A/He mice (20 females per group), over a period of 24 weeks, that
    received a total dose of methyl anthranilate of 2.25 or 11.2 g/kg bw
    (repeated i.p. injections three times a week for a total of 24
    injections). Methyl anthranilate was not considered to be a carcinogen
    under the conditions of this test (Stoner et al., 1973).

         A recent bioassay of anthranilic acid for possible
    carcinogenicity has shown that, under the conditions of the test,
    anthranilic acid was not carcinogenic for either Fisher 344 rats or
    B6C3F1 mice (DHEW, 1978).

    Acute toxicity

                                                                        

                                 LD50
    Animal          Route        mg/kg bw        References
                                                                        

    Mouse           oral         3 900           Jenner et al., 1964

    Rat             oral         2 910           Jenner et al., 1964

    Rat             oral         3 000           Dow, 1967

    Guinea-pig      oral         2 780           Jenner et al., 1964

    Guinea-pig      oral         4 000           Dow, 1967

    Rabbit          Dermal       5 000           Opdyke, 1974
                                                                        

    Short-term studies

    Rat

         Groups of 10 male and 10 female rats were maintained for 13 weeks
    on diets containing methyl anthranilate at levels of 0, 1000 and
    10 000 ppm (approximately equivalent to 50 and 500 mg/kg bw). No
    adverse effects were observed on body weights, appearance, food
    intake, haematology, organ weights, macroscopic or microscopic (at
    highest dietary level) examination of the major organs (Hagan et al.,
    1967).

         Groups of 10 male and 10 female weanling rats were maintained for
    a period of 115 days on diets containing methyl anthranilate at levels
    of 0, 3000 and 10 000 ppm (approximately equivalent to 150-300 and
    500-1000 mg/kg bw). There was no evidence of adverse effects at the
    3000 ppm level as judged by appearance, behaviour, growth, mortality,
    terminal haematological examination, final body weights, organ
    weights, and gross and microscopic examination. The only observable
    effects noted at the 10 000 ppm level were increases in the average
    weights of the liver and kidneys, and slight (minimal) histological
    changes in the kidneys (Dow, 1967).

         Groups of 35 male and 35 female rats received doses of 1.5 and
    3.0% of anthranilic acid in the diet for 78 weeks. There was a matched
    control group of 15 males and 15 females, which was part of a pooled
    control group of 30 males and 30 females.

         No increases in tumours were noted, nor were there any abnormal
    or dose-related non-neoplastic lesions. There was a slight dose-
    related depression of weight gain, but there were no unusual clinical
    signs, nor was there any effect on survival.

         Groups of 35 male and 35 female mice received doses of 2.5 and
    5.0% of anthranilic acid in the diet for 78 weeks. As in the rat
    experiment, there were matched and pooled control groups of 15 and 30
    of each sex.

         No increases in tumours were noted, nor were there abnormal or
    dose-related non-neoplastic lesions. Except for low-dose males, there
    was a slight dose-related depression of weight gain. There were no
    unusual clinical signs and there was no effect on survival (DHEW,
    1978).

    Comments

         The evaluation of methyl anthranilate is based on short-term
    toxicity studies and on data demonstrating the conversion of methyl
    anthranilate to methyl alcohol and anthranilic acid.

         Data from long-term studies in rats and mice with anthranilic
    acid show that there is no increase in tumour incidence in test
    animals compared with the controls. The previous conditional ADI was
    converted into an ADI. A monograph was prepared.

    EVALUATION

    Level causing no toxicological effect

    Rat: 3000 ppm (0.3%) in the diet equivalent to 150 mg/kg bw.

    Estimate of acceptable daily intake for man (ADI)

    0-1.5 mg/kg bw.

    REFERENCES

    Brown, R. R. & Price, J. M. (1956) Quantitative studies on metabolites
         of tryptophan in the urine of the dog, cat, rat, and man, J.
         Biol. Chem., 219, 985-997

    Charconnet-Harding, F., Dalgliesh, C. E. & Newberger, A. (1953) The
         relation between riboflavin and tryptophan metabolism, studied in
         the rat, Biochem. J., 53, 513-521

    DHEW (1978) Bioassay of anthranilic acid for possible carcinogenicity,
         US Department of Health, Education, and Welfare, DHEW Publication
         No. (National Institute of Health) 78-836

    Dow (1967) Toxicity of methyl anthranilate. Unpublished report from
         the Dow Chemical Company, Midland, Michigan, USA

    FAO/WHO (1967) Toxicological evaluation of some flavouring substances
         and non-nutritive sweetening agents, FAO Nutrition Meetings
         Report Series No. 44a; WHO/Food Add./68.33

    FAO/WHO (1968) Specifications for the identity and purity of food
         additives and their toxicological evaluation: some flavouring
         substances and non-nutritive sweetening agents, Eleventh Report
         of the Joint FAO/WHO Expert Committee on Food Additives, FAO
         Nutrition Meetings Report Series No. 44; World Health
         Organization Technical Report Series No. 383

    F.E.M.A. (1974) Scientific literature review of aliphatic primary
         alcohols, aldehydes, esters, and acids in flavor usage.
         Published by the National Information Services under contract
         with the Food and Drug Administration

    F.E.M.A. (1978) Scientific literature review of anthranilates in
         flavor usage. Published by the National Information Services
         under contract with the Food and Drug Administration

    Grundschober, F. (1977) Toxicological assessment of flavouring
         esters, Toxicology, 8, 387-390

    Hagan, E. C. et al. (1967) Food flavourings and compounds of related
         structure: II. Subacute and chronic toxicity, Food Cosmet.
         Toxicol., 5, 141-157

    Harger, R. N. (1967) Aliphatic alcohols, Prog. Chem. Tox., 3, 1-61

    Jenner, P. M. et al. (1964) Food flavourings and compounds of related
         structure. I. Acute oral toxicity, Food Cosmet. Toxicol., 2,
         327-343

    Longland, R. C., Shilling, W. H. & Gangolli, S. D. (1977) The
         hydrolysis of flavouring esters by artificial gastrointestinal
         juices and rat tissue preparations, Toxicology, 8, 197-204

    Opdyke, D. L. J. (1974) Fragrance raw materials monographs, Food
         Cosmet. Toxicol., 12, 935-936

    Price, J. M., Brown, R. R. & Ellis, M. E. (1956) Quantitative studies
         on the urinary excretion of tryptophan metabolites by humans
         ingesting a constant diet, J. Nutr., 60, 323-333

    Stoner, G. D. et al. (1973) Test for carcinogenicity of food additives
         and chemotherapeutic agents by the pulmonary tumor response in
         strain A mice, Cancer Res., 33, 3069-3085

    Williams, R. T. (1959) Detoxication mechanisms, The metabolism and
         detoxication of drugs, toxic substances and other compounds,
         London, Chapman & Hall Ltd, 2nd ed.
    


    See Also:
       Toxicological Abbreviations
       Methyl anthranilate (FAO Nutrition Meetings Report Series 44a)
       METHYL ANTHRANILATE (JECFA Evaluation)