Cover: The MAK Collection for Occupational Health and Safety

The MAK Collection for Occupational Health and Safety

Deutsche Forschungsgemeinschaft – Ständige Senatskommission zur Prüfung gesundheitsschädlicher Arbeitsstoffe (MAK-Kommission)

ISSN 2509-2383



2‐Propanol

MAK-Begründung, Nachtrag

  Andrea Hartwig1 (Vorsitz der Ständigen Senatskommission zur Prüfung gesundheitsschädlicher Arbeitsstoffe, Deutsche Forschungsgemeinschaft)
  MAK Commission2

1 Institut für Angewandte Biowissenschaften, Abteilung Lebensmittelchemie und Toxikologie, Karlsruher Institut für Technologie (KIT), Adenauerring 20a, Geb. 50.41, 76131 Karlsruhe, Deutschland
2 Ständige Senatskommission zur Prüfung gesundheitsschädlicher Arbeitsstoffe, Deutsche Forschungsgemeinschaft, Kennedyallee 40, 53175 Bonn, Deutschland

Abstract

The German Commission for the Investigation of Health Hazards of Chemical Compounds in the Work Area has re‐evaluated the maximum concentration at the workplace (MAK value) and the Pregnancy Risk Group of 2‐propanol [67‐63‐0].

In carcinogenicity studies no tumours were observed in rats and mice up to 5000 ml/m3. From the LOAEC in rats and mice of 2500 ml/m3 where narcotic effects were observed, a MAK value of 200 ml/m3 is derived also considering the increased respiratory volume at the workplace because the blood:air partition coefficient of 2‐propanol is > 5 (see List of MAK‐ and BAT Values, chapters I b and I c). Therefore, the MAK value of 200 ml/m3 is confirmed. At this concentration, no irritation is expected in humans based on the limited data in humans and animals.

Since a systemic effect is critical, Peak Limitation Category II is retained for 2‐propanol. Due to the half‐life of up to 2 hours in rats, the excursion factor of 2 is confirmed.

In developmental toxicity studies, 2‐propanol does not result in teratogenicity but in fetotoxicity at maternally toxic doses in rats and rabbits. According to a PBPK model and considering the increased respiratory volume at the workplace, the NOAEL of 600 mg/kg body weight in rats is scaled to a concentration of 1000 ml/m3. There is no PBPK model for rabbits but due to the similar NOAEL for developmental toxicity in rabbits the same concentration is supposed. Because fetotoxicity was only observed at maternally toxic doses, the difference of the NOAEC for fetotoxicity and the MAK value is sufficient so that 2‐propanol remains assigned to Pregnancy Risk Group C.


Keywords

2-Propanol, MAK-Wert, maximale Arbeitsplatzkonzentration, Entwicklungstoxizität, Spitzenbegrenzung, Reizwirkung