Registration Dossier
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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 468-670-0 | CAS number: -
- 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
Specific investigations: other studies
Administrative data
- Endpoint:
- specific investigations: other studies
- Adequacy of study:
- other information
Data source
Reference
- Reference Type:
- other: Body responsible for the test
- Title:
- Unnamed
Materials and methods
- Principles of method if other than guideline:
- Test procedure:
Animals: mouse CBA strain (females)
Test substance concentrations selected for the main study
were based on the results of a preliminary study.
In the main study, three groups of five experimental animals
were epidermally exposed to test substance concentrations
of 5%, 25% or 50% on three consecutive days. Five vehicle
control animals were similarly treated, but with vehicle
alone (Dimethyl sulphoxide).
Three days after the last exposure, all animals were
injected with 3H-methyl thymidine and after five hours the
draining (auricular) lymph nodes were excised.
After precipitating the DNA of the lymph node cells,
radioactivity measurements were performed. The activity was
expressed as the number of Disintegrations Per Minute (DPM)
and a stimulation index is calculated for each group.
Results and discussion
- Details on results:
- The irritation of the ears as shown by the animals, was
considered not to have a toxicologically significant effect
on the activity of the nodes.
All nodes of the experimental and control groups were
considered normal in size.
No macroscopic abnormalities of the surrounding area were
noted.
Mean DPM/animal values for the experimental groups treated
with test substance concentrations 5, 25 and 50% were 195,
164 and 126 respectively.
The mean DPM/animal value for the vehicle control group was
272.
The SI values calculated for the substance concentrations 5,
25 and 50% were 0.7, 0.6 and 0.5 respectively.
There was no indication that the test substance could elicit
an SI >= 3.
The six monthly reliability check with Hexylcinnamic
aldehyde indicates that the Local Lymph Node Assay as
performed at NOTOX is an appropriate model for testing for
contact hypersensitivity.
Applicant's summary and conclusion
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.