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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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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
Endpoint summary
Administrative data
Description of key information
Key value for chemical safety assessment
Skin sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
The sensitising activity of acetone was investigated under conditions applying open epicutaneous exposure. Due to the volatility of the test substance, after open dermal application the amount of applied test substance remaining on the skin and being available for dermal uptake is expected to be reduced.
Acetone was tested in a guinea pig maximization test (protocol of Magnusson and Kligman with modified scale for scoring of skin responses) with a group of 10 female Hartley guinea pigs. Induction was performed by intradermal injection and topical application of 100 % acetone. 21 days later the animals were challenged by topical application of 100 µl acetone on the shaved flank. No positive skin response was found in any of the animals. Acetone was used as vehicle for other test substances (Key study: Nakamura et al., 1994).
The sensitizing potential of acetone was further investigated in the mouse ear swelling assay. Induction consisted of topical application of acetone (100 %, day 0 and 2) to the right ear and scapular subcutaneous injection of 0.05 ml complete Freund's adjuvant (day 2). On day 9, left ear thickness was measured immediately before topical application of the test substance on both sides of the ear, and again 24 hours later (day 10). There was no increase of ear thickness indicating absence of a sensitizing potential (Supporting study: Descotes, 1988).
Additionally, from skin prick tests with human probands using acetone as solvent for other test substances there are no indications of a sensitizing potential. Principally, concerning the used amounts in skin prick tests, a degreasing of the skin and the minor irritation are negligible (for details see Section 7.10.4).
Migrated from Short description of key information:
Guinea pig maximization test: negative (Key study: Nakamura et al., 1994)
Mouse ear swelling assay: negative (Supporting study: Descotes, 1988)
Justification for classification or non-classification
Skin sensitisation: based on negative test results in animal test systems and based on human experience there is no classification of acetone for skin sensitisation
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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