Registration Dossier
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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 946-682-1 | 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
Endpoint summary
Administrative data
Description of key information
According to ECHA Guidance Chapter R.11 Version 3.0 (June 2017), the Bioaccumulation criterion is unlikely to be triggered for substances with a log Kow higher than 10.
Indeed, for highly hydrophobic substances, like the registered substance with a log Kow > 6, experimentally derived BCF values tend to decrease with increasing log Kow. Several explanations of this breakdown of linerarity can be given. Conceptual explanations of this non-linearity mainly refer to either biotransformation, reduced membrane permeation kinetics or reduced biotic lipid solubility for large molecules. A low bioavailability and uptake of these substances in the organism will thus occur. Other factors comprise experimental artefacts, such as equilibrium not being reached, reduced bioavailability due to sorption to organic matter in the aqueous phase, and analytical errors. In addition, as the registered substance is readily biodegradable, it is quite likely that, in an experimental study (via food or water), a low bioavailability, a metabolic hydrolysis and a reduced membrane uptake rate will thus occur. The uptake by oral route is more critical (dietary fedding study). In this case, the substance is likely to be broken in the gut and any bioaccumulation would be due to oral consumption of the narcotic by-products and the weak acid.
To confirm that no bioaccumulation is expected for the registered substance considering the high hydrophobic properties and rapid metabolisation (ester hydrolysis) of the substance, QSAR prediction using Arnot-Gobas methodology was performed, including biotransformation rate estimates. The estimated BCF values were all comprised between 0.94 and 9.42 L/kg. The registered substance is not bioaccumulable according to CLP (BCF < 500) and PBT criteria (BCF < 2000). However, based on restrictions on the applicability domain, these predictions are considered rather as qualitative than quantitative.
Also, the registered substance presents no toxicity for mammals. The "No Observed Adverse Effect Level", NOAEL, was determined at the highest tested dose in the sub-acute toxicity study and sub-chronic oral toxicity studies. This observation confirm the limit absorption and therefore the limited bioaccumulation of the registered substance.
Additional information
According to the key biodegradation study, no transformation product was detected at the end of the 28-day test period. Therefore, the evaluation of the bioaccumulation potentiel of the transformation product(s) is not relevant.
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.