MEIC Evaluation of Acute Systemic Toxicity

Author:

Ekwall Björn11,Barile Frank A.21,Castano Argelia31,Clemedson Cecilia11,Clothier Richard H.41,Dierickx Paul51,Ekwall Barbro11,Ferro Margherita61,Fiskesjö Geirid71,Garza-Ocañas Lourdes81,Gómez-Lechón Maria José91,Gülden Michael101,Hall Tony111,Isomaa Boris121,Kahru Anne131,Kerszman Gustaw141,Kristen Udo151,Kunimoto Manabu161,Kärenlampi Sirpa171,Lewan Lillemor181,Loukianov Anatoly191,Ohno Tadao201,Persoone Guido211,Romert Lennart221,Sawyer Thomas W.231,Shrivastava Ravi241,Segner Helmut251,Stammati Annalaura261,Tanaka Noriho271,Valentino Matteo281,Walum Erik221,Zucco Flavia291

Affiliation:

1. CTLU, Pavals, När, 620 13 Stånga, Sweden

2. Department of Natural Sciences, York College, City University of New York, 94–20 Guy R. Brewer Boulevard, Jamaica, NY 11451, USA

3. Environmental Toxicology, Centro de Investigacion en Sanidad Animal, Valdeolmos, 28130 Madrid, Spain

4. School of Biomedical Sciences, Queen's Medical Centre, Nottingham NG7 2UH, UK

5. Instituut voor Hygiene en Epidemiologie, Juliette Wytsmanstraat 14, 1050 Brussels, Belgium

6. Institute of General Pathology, Via L.B. Alberti 2, 16132 Genova, Italy

7. Department of Genetics, University of Lund, Sölvegatan 29, 223 62 Lund, Sweden

8. Departament de Farmacologia y Toxicologia, Facultad de Medicina, Universidad Autonoma de Nuevo Leon, Apartado Postal No. 146, Col. del Valle, Nuevo Leon, Mexico

9. Cultivos Celulares, Centro Investigacion, Hospital La Fe, Av. Campanar 21, 46009 Valencia, Spain

10. Institut für Toxicologic, Zelltoxikologie, Christian-Albrechts-Universität, Weimarer Strasse 8, Haus 3, 24106 Kiel, Germany

11. MD Laboratories, B.P. 30, 68870 Bartenheim, France

12. Department of Biology, Åbo Akademi University, Biocity, Artillerigatan 6, 20520 Abo, Finland

13. Laboratory for Molecular Genetics, Institute of Chemical Physics & Biophysics, Estonian Academy of Sciences, Akadeemia tee 23, EE-0026 Tallinn, Estonia

14. Institute of Life Science and Chemistry, P.O. Box 260, 4000 Roskilde, Denmark

15. Institut für Allgemeine Botanik, Universität Hamburg, Ohnhorststrasse 18, 22609 Hamburg, Germany

16. Environmental Health Sciences Division, National Institute of Environmental Studies (NIES), 16-Z Onogawa, Tsukuba, Ibaraki 305, Japan

17. Department of Biochemistry and Biotechnology, University of Kuopio, P.O. Box 1627, 702 11 Kuopio, Finland

18. Department of Animal Physiology, University of Lund, Helgonavägen 3D, 223 62 Lund, Sweden

19. CETA - Centre for Ethical Treatment of Animals, 39-3-23, Volzsky Bulvar, 109462 Moscow, Russia

20. RIKEN Cell Bank, Institute of Physical and Chemical Research (RIKEN), 3-1-1 Koyadai, Tsukuba City, Ibaraki 305, Japan

21. Laboratory for Biological Research in Aquatic Pollution, University of Ghent, J. Plateaustraat 22, 9000 Ghent, Belgium

22. Pharmacia & Upjohn, 112 87 Stockholm, Sweden

23. Biomedical Defence Section, Defence Research Establishment Suffield–DRES, Box 4000, Medicine Hat, Alberta T1A 8K6, Canada

24. Vitro-Bio, 11, Allée de la Source, 63340 Le Breuil-Sur-Couze, France

25. Umweltforschungs-zentrum, Leipzig-Halle GmbH, Sektion für Chemische Ökotoxikologie, PF-2, 04301 Leipzig, Germany

26. Department of Comparative Toxicology and Ecotoxicology, Istituto Superiore di Sanita, Viale Regina Elena 299, 00161 Roma, Italy

27. Hatano Research Institute, Food and Drug Safety Center, 729-5 Ochiai, Hadano, Kanagawa 257, Japan

28. Universitá di Ancona, Clinica del Lavoro, Ospedale Regionale, 60020 Ancona, Italy

29. Istituto Tecnologie Biomediche, Consiglio Nationale delle Recherche, Via G.B. Morgagni 30/E, 00161 Roma, Italy.

Abstract

The Multicenter Evaluation of In Vitro Cytotoxicity (MEIC) programme was set up to evaluate the relevance for human acute toxicity of in vitro cytotoxicity tests. At the end of the project in 1996, 29 laboratories had tested all 50 reference chemicals in 61 cytotoxicity assays. Five previous articles have presented the in vitro data and the human database to be used in the evaluation. This article presents three important parts of the final evaluation: a) a comparison of rat and mouse oral LD50 with human acute lethal doses for all 50 chemicals; b) a display of the correlations between IC50 (concentration causing 50% inhibition) values from all 61 assays and three independent sets of human acute lethal blood concentrations, i.e. clinical lethal concentrations, forensic lethal concentrations, and peak concentrations; and c) a series of comparisons between average IC50 values from ten human cell line 24-hour assays and human lethal blood concentrations. In the latter comparisons, results from correlations were linked with known human toxicity data for the chemicals, to provide an understanding of correlative results. This correlative/mechanistic approach had the double purpose of assessing the relevance of the in vitro cytotoxicities, and of testing a series of hypotheses connected with the basal cytotoxicity concept. The results of the studies were as follows. Rat LD50 predictions of human lethal dosage were only relatively good (R2 = 0.61), while mouse LD50s gave a somewhat better prediction (R2 = 0.65). Comparisons performed between IC50 values from the 61 assays and the human lethal peak concentrations demonstrated that human ceil line tests gave the best average results (R2 = 0.64), while mammalian and fish cell tests correlated less well (R2 = 0.52–0.58), followed by non-fish ecotoxicological tests (R2 = 0.36). Most of the 61 assays underpredicted human toxicity for digoxin, malathion, carbon tetrachloride and atropine sulphate. In the correlative/mechanistic study, the 50 chemicals were first separated into three groups: A = fast-acting chemicals with a restricted passage across the blood–brain barrier; B = slow-acting chemicals with a restricted passage across the blood–brain barrier; and C = chemicals which cross the blood–brain barrier freely, while inducing a non-specific excitation/depression of the central nervous system (CNS). The IC50 values for chemicals in group C were divided by a factor of ten to compensate for a hypothetical extra vulnerability of the CNS to cytotoxicity. Finally, the average human cell line IC50 values (24-hour IC50 for groups A and C, and after 48-hour for group B) were compared with relevant human lethal blood concentrations (peak concentrations for groups A and C, and 48-hour concentrations for group B). As a result, in vitro toxicity and in vivo toxicity correlated very well for all groups (R2 = 0.98, 0.82 and 0.85, respectively). No clear overprediction of human toxicity was made by the human cell tests. The human cell line tests underpredicted human toxicity for only four of the 50 chemicals. These outlier chemicals were digoxin, malathion, nicotine and atropine sulphate, all of which have a lethal action in man through interaction with specific target sites not usually found in cell lines. Potassium cyanide has a cellular human lethal action which cannot be measured by standard anaerobic cell lines. The good prediction of the human lethal whole-blood concentration of this chemical was not conclusive, i.e. was probably a “false good correlation”. Another two chemicals in group C resulted in “false good correlations”, i.e. paracetamol and paraquat. The comparisons thus indicated that human cell line cytotoxicities are relevant for the human acute lethal action for 43 of the 50 chemicals. The results strongly support the basal cytotoxicity concept, and further point to the non-specific CNS depression being the obligatory reaction of humans to cytotoxic concentrations of chemicals, provided that the chemicals are able to pass the blood–brain barrier.

Publisher

SAGE Publications

Subject

Medical Laboratory Technology,Toxicology,General Biochemistry, Genetics and Molecular Biology,General Medicine

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