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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 206-007-7 | CAS number: 286-20-4
- 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
Link to relevant study record(s)
Description of key information
Short description of key information on bioaccumulation potential result:
The bioaccumulation potential of the test material was shown, by both in vivo and in vitro methods, to be very low. Regardless of the route of exposure the test material was readily excreted predominantly in the urine; there was little absorption and the test material was readily metabolised.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
Three studies have been provided to address the bioaccumulation endpoint on a weight of evidence basis.
Jerina (1968) assessed the metabolism of the test material in an in vitro study. The test material was incubated with a microsomal preparation of rabbit liver. Under the conditions of the test it was determined that the test material was hydrolysed by the liver enzyme, epoxide hydrase to form the metabolite 1,2-cyclohexanediol. Sauer (1977) assessed the absorption, distribution, metabolism and excretion of radiolabelled test material in vivo. There were three parts to the study; radiolabelled test material was dosed orally, dermally and intravenously. Both rats and mice were exposed in the oral and dermal applications; only rats were used for the intravenous exposure. Regardless of the route of exposure the test material was predominantly excreted in the urine, there was little absorption and the test material was readily metabolised. Both Jerina (1968) and Sauer (1977) were performed to sound scientific principles and have been assigned a reliability score of 2, according to the principles of assessing data accuracy set out in Klimisch (1977).
Foulger (1948) has also been provided as supporting data. During the study, rabbits were exposed to the test material via topical application. The minimum fatal dose was determined to be > 6ml/kg. The low absorption was considered to be caused by the rapid evaporation from the surface of the skin. The study have been assigned a score of 4, according to Klimisch (1977), as there is incomplete reporting of methodology and thus it is not possible to assess the accuracy of the data.
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.