FAO Nutrition Meetings Report Series No. 48A WHO/FOOD ADD/70.39 TOXICOLOGICAL EVALUATION OF SOME EXTRACTION SOLVENTS AND CERTAIN OTHER SUBSTANCES The content of this document is the result of the deliberations of the Joint FAO/WHO Expert Committee on Food Additives which met in Geneva, 24 June -2 July 19701 Food and Agriculture Organization of the United Nations World Health Organization 1 Fourteenth report of the Joint FAO/WHO Expert Committee on Food Additives, FAO Nutrition Meetings Report Series in press; Wld Hlth Org. techn. Rep. Ser., in press. ACETONE Biological Data Biochemical aspects Acetone is readily absorbed by solution into the blood after inhalation (Kagan, 1924) and progressive accumulation in tissues has been noted after 6 hours inhalation (Haggard et al,, 1944). Skin absorption occurs only slowly in animals (Lazarew et al., 1931). Large oral doses are mostly excreted unchanged through the lungs (40-70%) and the kidneys (15-30%) but small amounts are metabolised slowly to formate and acetate within 24 hours (Williams, 1959). Dogs excrete in their urine some 1-4% of acetone when administered orally at rates of 0.2-1.6 g/kg. Some 60% is excreted through the lungs (Schwarz, 1898). Small doses (1.7 mg/kg body weight) are oxidised mainly to CO2 (53%) while some 7-14% is exhaled unchanged (Price & Rittenberg, 1950; Sakami & Lafaye, 1950). Acetone labelled with C14 in the methyl group was shown to be converted by rats to liver glycogen, serine, choline and methionine via formate and acetate (Sakami & Lafaye, 1950), while another metabolic pathway involved direct conversion to pyruvate in the liver (Sakami & Lafaye, 1951). Acetone injected into dogs produced high hepatic levels of ß-hydroxybutyric acid (Valdiguie, 1935). Of 1 g. administered to man some 24% are excreted through the lungs (Rothkopf, 1936). I.v. injection into rabbits markedly increased acetoacetic acid and ß-hydroxybutyric acid and glucose levels in their blood (Caccuri, 1937). After i.v. injection at constant rate of 10 g acetone into man over 2 hours some 110 mg were lost through the lungs (1 normal, 5 diabetic subjects). Total urinary ketone excretion did not rise significantly in 7 fasting normal subjects but some 360 mg acetone were excreted in 24 hours by this route. 12 normal subjects maintained high blood levels of acetone for 4 hours after injection but almost all had disappeared from the blood after 24 hours. Acetoacetic acid levels rose less high in the blood and also remained elevated for 4 hours after injection. No ß-hydroxybutyric acid appeared. Simultaneous i.v. glucose or i.v. insulin did not affect blood acetone levels in 7 normal fasting subjects. I.v injection of acetone into 12 diabetics showed similar levels as in 19 normal subjects. Hence no impairment in ability to destroy acetone occurs in diabetics. The rate of breakdown is so slow, however, as to preclude that more than a small part of normal fat metabolism passes through an acetone stage (Koehler et al., 1941). The rat and the dog excrete acetone from the blood at approximately similar rates (Abshagen & Rietbrock. 1969). Acute toxicity Animal Route LD50 LD100 References mg/kg mg/kg bodyweight bodyweight Mouse inhalation - 46000 ppm Schultze, 1932 oral 10700 - (Smyth et al., 1962 (Shell Chemical Co., 1969 9700 - Spector, 1956 i.v. - 4ml/kg Walton et al., 1928 inhalation - 32000 ppm/ (Smyth et al., 1962 4 hrs (Shell Chemical Co., 1969 Rabbit intragastric 5340 - Spector, 1956 - 5-10ml/kg Walton et al., 1928 i.v. - 6-8 ml/kg Walton et al., 1928 percutaneous > 20 ml/kg - (Smyth et al., 1962 (Shell Chemical Co., 1969) Dog intragastric - 8 g/kg Albertoni, 1884 The acute effects of acetone are essentially that of a fairly strong anaesthetic (Browning, 1965). Repeated intragastric administration of 8 ml to rabbits for 5-22 days or 8-10 ml to dogs for 8-35 days produced albuminuria and epithelial necrosis of convoluted renal tubules (Albertoni and Pisenti, 1887). Daily administration of 1-2.5 g/kg acetone intragastrically to 5 dogs for 9-19 days produced nephritis with tubular destruction (Poliak, 1925). Special tests Mouse Acetone was painted on the clipped dorsal skin of 60 female mice three times a week for 447 days (64 weeks) as part of another experiment. No local papillomata or carcinomata were seen (van Duuren et al., 1965). Rat The single injection of 0.1 ml, as part of another experiment, into one or both salivary glands of 35 male and 7 female rats produced local necrosis and complete regenerative repair after 3 weeks. Animals observed for 8 months showed no local or distant tumour formation either macroscopically or histologically (Cherry & Glücksmann, 1965). Chicken At dose levels of 39, and 78 mg/egg hatchability of fresh fertile unincubated eggs injected into the yolk sac was reduced to 76% and 47% of the normal (McLaughlin et al., 1964). Preincubation injection of a maximum dose of 0.1 ml/egg resulted in a 37% hatch, the remainder being killed due to yolk coagulation. The hatchability of 3 days incubated eggs injected at similar doses was reduced to 20% (Waller, 1967). Observations in man Widespread industrial use over many years (e.g. 2000 ppm inhaled for 15 years) only yielded a few cases of mild intoxication, but no reports of permanent haematological or organ damage (Browning 1965; Rowe & Wolf, 1963; Fassett, 1963). Reversible effects resulting from high oral doses occur on liver and kidney and are manifest by albuminuria, presence of red and white cells in urine sediment, urobilinuria. and increased serum bilirubin, Acute lethal doses are estimated to be about 50 ml/man and death is a result of respiratory depression, (API Toxicological Reviews. 1955). The TLV is 1000 ppm (Amer. Conf. Gov. Industr. Hygienists, 1969). 15.20g given orally daily to man over several days produced only slight drowsiness but no other ill effects (Albertoni, 1884). Acute massive intoxication in man has caused collapse and possible liver and kidney injury (Sack, 1940, Smith & Mayers, 1944, Harris & Jackson, 1952). Dermatitis from frequent sustained skin contact and irritation of eyes and the nasal mucosa have been observed in man (Browning 1965). Some 10% of inhaled acetone is excreted through human skin (Parmeggiani & Sassi, 1954). Comments The principal toxic action of large doses results in narcosis and repeated smaller doses have produced headache, drowsiness and irritation of eyes and mucosal surfaces in man. There is minor circumstantial evidence of some toxic effect on the liver and kidney in man after acute massive intoxication. Early findings suggest severe toxicity in dogs and rabbits on prolonged oral administration of large doses. The small amounts likely to be found as residues in food are probably oxidised and metabolized by well known pathways. Many years of human industrial experience have shown no evidence of significant organ damage. Tentative Evaluation The use of this solvent should be restricted to that determined by good manufacturing practice, which is expected to result in minimal residues. Within these limits residues are unlikely to have any significant toxicological effect. REFERENCES 1. Abshager, U & Rietbrock, N. (I969) N. Schmied. Arch. Pharmak., 264, 110 2. Albertoni, P. (1884) Arch. Exptl. Pathol. Pharmakol., 18, 219 3. Albertoni, P. & Pisenti, G. (1887) Arch. Exptl. Pathol. Pharmakol 23. 393 4. Amer. Conf. Gov. Ind. Hyg. (1969) Threshold limit values for 1969 5. A.P.I. Toxicological Review (1965) Unpublished data 6. Browning, E. (1965) Toxicity and metabolism of industrial solvents, Elsevier, Amsterdam 7. Caccuri, S. (1937) Biochim. e terap. sper., 24, 168 8. Cherry, C.P. & Glüksmarn, A. (1965) Brit. J. Cancer, 19 287 9. Fassett, D.W. (1963) in F.A. Patty, Industrial Hygiene and Toxicology (1963) Vol.11 10. Haggard, A.W., Greenberg, L.A. & Turner, J.M. (1944) J. Ind. Hyp. Toxilcol., 26, 133 11. Harris, L.C. & Jackson, R.H. (1952) B.M.J., 2, 1024 12. Kagan, E. (1924) Arch. Hyg. Berlin, 94, 41 13. Koehler, A.E., Windsor, E. & Hill, E. (1941) J. Biol. Chem., 140, 811 14. Lazarew, N.U., Brussilowskaja, A.J. & Lawrow, J.M. (1931) Arch. Gewerbepathol. Gewerbehyg., 2, 641 15. McLaughlin, J. et al. (1964) Amer. Ind. Hyg. Ass. J., 25, 282 16. Parmeggiani, L. & Sassi, C. (1954) Med. Lavoro, 45, 431 17. Poliak, B. (1925) Arch. Exptl. Path. Pharmakol., 205, 220 18. Price, T.O. & Rittenberg, D. (1950) J. Biol. Chem., 185, 449 19. Rothkopf, H. (1936) Z. ges exp. Med., 99 464 20. Rowe, V.K. & Wolf, M.A. (1963) in F.A. Patty, Industrial Hygiene and Toxicology (1963) Vol.II 21. Sack, G. (1940) Arch. Gewerbepathol. Gewerbehyg., 10, 80 22. Sakami, W. & Lafaye, J.M. (1950) J. Biol. Chem., 187, 369 23. Sakami, W. & Lafaye, J.M. (1951) J. Biol. Chem., 193, 199 24. Schultze, D. (1932) Dissertation, Univ. Würzburg 25. Schwarz, L. (1898) Arch. Exptl. Pathol. Pharmakol., 40, I68 26. Shell Chemicals Co. (1969) Industr. Hyg. Bull., 69-10 27. Smith, A.R. & Mayers, M.R. (1944) Ind. Bull, New York, State Dept. Labor., 23, 174 28. Smyth, H.F. Jr. et al. (1962) Ind. Hyg. J., 23, 95 29. Spector, W.S. (1956) Handbook of Toxicology, Vol.1 30. Valdiguie, P. (1935) Compt. rend. Soc. biol 118 858 31. Van Duuren, B.L., Orris, L. & Nelson, N. (1965) J. Nat. Conc. Inst., 35, 707 32. Walker, N.E. (1967) Tox. appl. Pharm., 10, 290 33. Walton, D.C., Kehr, E.F, & Loevenhart, A.S. (1928) J. Pharm. Exptl. Ther., 33, 175 34. Williams, R.T. (1959) Detoxication Mechanisms, Chapman & Hall, London
See Also: Toxicological Abbreviations Acetone (EHC 207, 1998) Acetone (ICSC) ACETONE (JECFA Evaluation)