Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 204-634-0 | CAS number: 123-54-6
- 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
Long-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
The NOEC of Acetyl acetone for the early life stages of fathead minnow fish is 10 mg/l. The LOEC was 22 mg/l.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 10 mg/L
Additional information
Fish early-life stage (ELS) toxicity test with Acetyl acetone (flow-through).
This study investigated the effects of Acetyl acetone on survival, development and growth during the early stages of the fish species fathead minnow. The study procedures described in this report were based on the OECD guidelines for Testing of Chemicals: Guideline No. 210, 1992. In addition, the procedures were designed to meet the test methods and validity criteria of the EPA Ecological Effects Test Guidelines, 'Public Draft', EPA 712-C-96-121, 1996.
The batch of Acetyl acetone tested was a clear colourless liquid with a purity of 99.8% and completely soluble in test medium at the concentrations tested.
Based on the results of an 8-day preliminary test and a limit test, a final ELS test was performed with a control group and Acetyl acetone target concentrations of 1.0, 2.2, 4.6, 10 and 22 mg/l. The test started by placing sixty fertilised eggs per test group, randomly distributed and divided equally over three stainless steel test vessels (3 replicates/test concentration) in a flow-through system. The total test period was 34 days. Samples for analytical confirmation of actual exposure concentrations were taken before the start of the exposure, at the start of exposure and weekly thereafter. Analyses were based on Total Organic Carbon (TOC) concentrations.
TOC-analyses generally confirmed correct functioning of the flow-through system and therefore it was considered justified to base all test results on the target concentrations.
Acetyl acetone did not induce any significant, visible effects on the development and survival of fathead minnow embryos and did not significantly affect time of hatching or the hatching success in any of the concentrations tested.
Average larval survival in the control group was 73%. Larval survival in the Acetyl acetone treatments ranged between 70 and 94% and was not statistically different from the control. No significant treatment related sub-lethal effects were observed.
Length and weight of the fish in the test group of 22 mg/l was statistically significantly reduced compared to the control group at the end of the test period. Growth in the lower concentrations was not significant different from the control group.
The study met the acceptability criteria prescribed by the protocol and the guidelines and was considered valid.
The results of the final flow-through test led to the following conclusions for Acetyl acetone:
1. Acetyl acetone did not induce any significant, visible effects on the development of fathead minnow embryos at concentrations up to and including 22 mg/l.
2. Acetyl acetone did not significantly affect time of hatching or the hatching success up to and including 22 mg/l.
3. Acetyl acetone did not affect survival or development of the larvae during the whole test period up to and including 22 mg/l.
4. Acetyl acetone affected growth of the larvae during the 34-day test period at the highest test concentration of 22 mg/l.
Hence, the NOEC of Acetyl acetone for the early life stages of fathead minnow fish is 10 mg/l. The LOEC was 22 mg/l.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.