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EC number: 200-662-2 | CAS number: 67-64-1
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Neurotoxicity
Administrative data
Description of key information
Oral exposure: rat, up to 9 w exposure: NOAEL 650 mg/kg bw/d
rat, 4 w exposure: LOAEL 1,300 mg/kg bw/d
Inhalation: rat, acute 4 hr: NOAEC 9,500 mg/m3
rat, 13 w exposure: NOAEC 9,500 mg/m3 = NOAEL 1,000 mg/kg bw/d
Key value for chemical safety assessment
Effect on neurotoxicity: via oral route
Endpoint conclusion
- Dose descriptor:
- NOAEL
- 650 mg/kg bw/day
Effect on neurotoxicity: via inhalation route
Endpoint conclusion
- Dose descriptor:
- NOAEC
- 9 500 mg/m³
Additional information
There is no study on neurotoxicity available that is similar to a guideline study. The available reliable studies investigated single endpoints of neurotoxicity or behavioural toxicity and are altogether evaluated for a weight of evidence approach.
Oral exposure of male Wistar rats in drinking water studies for 4 to 9 weeks
After exposure to 10,000 mg acetone/L water for 4 weeks or to 5,000 mg acetone/L water for 9 weeks (corresponding to doses of 1,300 or 650 mg/kg bw/d, neurobehavioural toxicity was screened via a Functional Observation Battery, and weight and histopathology of the brains was examined. The only neurobehavioural effect found after the 4-week exposure to 10,000 mg/L was reduced hindlimb and forelimb grip strengths, with a significant effect on the former parameter only. The NOAEL for neurobehavioural toxicity corresponded to a dose of 650 mg/kg bw/d (9 week exposure), the LOAEL was 1,300 mg/kg bw/d (4 week exposure) (Dalgaard et al., 1999).
After dosing of rats with 5000 mg acetone/L water for 6 weeks (dose of ca. 600 mg/kg bw/d), the only effect was a slight although significant decrease of the nerve conduction velocity in acetone-treated rats compared to controls after 6 weeks of treatment (29.5 ± 1.1 vs. 31.5 ± 2.1 m/sec, P<0.05). However, as at the same timepoint the nerve conduction velocity in the acetone group showed the highest value measured at any timepoint from treatment week 3 to 6, a possible adverse neurophysiological effect is highly questionable. Weekly monitoring of behaviour as performance on a rotarod was without a significant finding (Ladefoged et al., 1989). Consequently, the resulting NOAEL of ca. 600 mg/kg bw/d is at a comparable level as in the study of Dalgaard et al. (1999).
13 -week inhalation of acetone by whole-body exposure
Groups of 10 adult male Crl:CD BR rats were used to assess whether inhalation of 0, 1,000, 2,000, or 4,000 ppm of acetone vapour (ca. 0, 2375, 4750 or 9500 mg/m3corresponding to doses of ca. 0, 250, 500, or 1000 mg/kg bw/d) for 13 weeks, 5 days/week, 6 hrs/day altered schedule-controlled operant performance. Up to 4000 ppm, acetone vapour does not appear to have enduring effects on nervous system functions that mediate the performance of a complex, learned task, that is lever-pressing on a multiple fixed-ratio-interval schedule of food presentation after extensive training (Christoph et al., 2003).
Justification for classification or non-classification
No classification according to EC regulation 1272/2008 is warranted.
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