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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 700-380-4 | 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
Additional information
Bioconcentration factor (BCF):
When measured BCF values are not available, a BCF may be predicted from the relationship between Pow and BCF. According to ECHA guidance, the most common and simplest QSAR models are based on correlations between BCF and chemical hydrophobicity (as modelled by logPow). The mechanistic basis for this relationship is the analogy of the partitioning process between lipid-rich tissues and water to that between n-octanol and water (whereby n-octanol acts as a lipid surrogate). In this model, uptake is considered to be a result of passive diffusion through gill membranes.
Based on the QSAR calulation (EpiSuite - KOWWIN v1.67) logPows for C16 and C18 component was determined as follows: 11.2 (Hexadecyl nonanoate) and 12.2 (Octadecyl nonanoate); mean value: 11.7.
Nevertheless, the logPow of 11.7 (mean value) is out of the applicability domain of this calcualtion and thus according to EpiSuite – BCFBAF v.3.01 “user Guide help”: “bioconcentration factor estimates are less accurate for compounds outside the MW and logPow ranges of the training set compounds.”Furthermore, it should be considered that“BCF estimates have more instances of a given correction factor than the maximum for all training set compounds.”
However, according to ECHA guidance on information requirements and chemical safety assessment - chapter R.11: PBT assessment, May 2008, “at very high logPow (>6), a decreasing relationship between the two parameters (logPow and logBCF) is observed. Apart from experimental errors in the determination of BCF values for these very hydrophobic chemicals, reduced uptake due to the increasing molecular size may play a role as well. Moreover, the experimental determination of logPow for very hydrophobic chemicals is normally also very uncertain due to experimental difficulties (...) The aquatic BCF of a substance is probably lower than 2000 L/kg if the calculated logPow is higher than 10.”
Based on this, it can safely be assumed that the BCF of SymMollient® S is below 2000 L/kg ww
Biomagnification factor (BMF):
No experimental data are available. According to ECHA guidance, the availability of measured BMF data on predatory organisms is very limited at present and so the provided default values should be used as a screening approach designed to identify substances for which it may be necessary to obtain more detailed information. Accordingly, the default BMF value is 1 (BCFfish < 2,000) for organic substances with a logPow >9. Therefore, biomagnification appears to be low.
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.