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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 203-825-6 | CAS number: 111-01-3
- 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
According to the BCF/BAF methods, the regression based method calculates a BCF of 3 and the Arnot-Gobas method predicts a BCF of 0.89. Therefore these values are consistent and predict that the substance is non-bioaccumulable, supporting the expectations from the highlog KOWand rapid biodegradability.
Additional information
ANSWER TO TESTING PROPOSAL DECISION number: TPE-D-2114314157-57-01/F
No direct information is available on the BCF of the substance in fish or other organisms. Furthermore, indirect information on physico-chemical properties is not experimentally available due to the extreme hydrophobicity of this substance. The solubility cannot be experimentally measured and the estimate of thelog KOWis inadequate as based on 1) a simple ratio of octanol and water solubilities rather than a genuine partition value and 2) a less than value for solubility which has been calculated to be overestimated by several orders of magnitude.
Nevertheless, these data can be used in a weight of evidence approach to justify waiving a BCF study. First, a standard BCF study would not be technically possible to perform due to the insolubility of the test substance such that it would not be possible to maintain the test solution concentration. Therefore the only option would be to perform a fish dietary accumulation study which in itself cannot directly provide a BCF value. With a predictedlog KOWof 17, the substance is well beyond the threshold for potential B or vB according to ECHA PBT guidance. Moreover, Squalane has been shown to be readily biodegradable and, as a long chain hydrocarbon, may be expected to be rapidly metabolized by fish. Thus, a modelling approach is considered sufficient as an alternative to an experimental method in this case. According to the BCF/BAF methods, the regression based method calculates a BCF of 3 and the Arnot-Gobas method predicts a BCF of 0.89. Therefore these values are consistent and predict that the substance is non-bioaccumulable, supporting the expectations from the highlog KOWand rapid biodegradability.
For all the above reasons, studies on Bioaccumulation of Squalane are not considered scientifically justifiable.
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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