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Diss Factsheets
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EC number: 927-870-2 | 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
- Endpoint:
- bioaccumulation in aquatic species: fish
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
- Conclusions:
- Considering REACH Annex IX 9.3.2 criteria, bioaccumulation in aquatic species, preferably fish, may be proposed. However, as the substance is poorly soluble in water, exposure of the aquatic compartment is unlikely: this test is not proposed to be performed.
The substance is an UVCB which is insoluble in water, so test methods are not applicable.
The log Kow ranging 2.4- 7.7 for individual components of the substance suggests a high bioaccumulation potential. BCF is below 2000.
However, no accumulation of the substance is expected based on the various metabolic pathways and excretion routes which can be expected for the substance. - Executive summary:
The study to determine the partition coefficient (log KOW) gives data ranging from 2.4 to 7.7, indicating high bioaccumulation potential.
The substance contains about 85 % of 1-hexadecanol (log KOW = 6.7) and 1-octadecanol (log KOW= 7.7). The alkyl chain length has the highest impact on the log KOW value.
A quantitative estimation of the bioconcentration factor (BCF) for fish can be performed according to the parabolic equation given in the Guidance on information requirements and chemical safety assessment (Chapter R.7c) for substances having a log Pow > 6 (with log KOW = 7.7):
Parabolic equation:
log BCFfish = -0.20 x (log KOW)² + 2.74 x log KOW – 4.72
log BCFfish = -0.20 x (7.7)² + 2.74 x 7.7 – 4.72
log BCFfish = 4.52
BCFfish = 33 113 L/kg
A BCF of 224 L/kg was estimated by BCFWIN using log KOW of 7.7. However, this method delivers many underestimations of BCFs. Hence, this QSAR-method is not reliable for estimating the bioaccumulation potential of the substance.
BCFWIN and equation lead to very different results.
Considering REACH Annex IX 9.3.2 criteria, bioaccumulation in aquatic species, preferably fish, may be proposed. However, as the substance is poorly soluble in water, exposure of the aquatic compartment is unlikely: this test is not proposed to be performed. The substance is an UVCB which is insoluble in water, so test methods are not applicable. The log Kow ranging 2.4- 7.7 for individual components of the substance suggests a high bioaccumulation potential. BCF is below 2000. However, no accumulation of the substance is expected based on the various metabolic pathways and excretion routes which can be expected for the substance.
Reference
Description of key information
Considering REACH Annex IX 9.3.2 criteria, bioaccumulation in aquatic species, preferably fish, may be proposed. However, as the substance is poorly soluble in water, exposure of the aquatic compartment is unlikely: this test is not proposed to be performed. The substance is an UVCB which is insoluble in water, so test methods are not applicable. The log Kow ranging 2.4- 7.7 for individual components of the substance suggests a high bioaccumulation potential.
Furthermore, with regard to metabolic pathways of alkyls polyglucosides and fatty alcohols, it is anticipated that alkyl polyglycosides are 100% absorbed by oral ingestion, followed by ready hydrolysis and metabolism of the resulting cleavage products, sugar and fatty alcohol, in common mammalian physiological pathways. And long chained alcohols are generally highly efficiently metabolised and there is limited potential for retention or bioaccumulation for the parent alcohols and their biotransformation products (see section 7.1).
In addition, in fish, it is suggested that the fatty alcohol in various tissues of carp, which seems to be a substrate of acyl CoA: alcohol acyltransferase, is one of the most important key precursor to form wax esters. And wax esters have been known for a long
time as a prominent lipid class of some aquatic animals. (Mankura et al., 1986; Mankura et al., 1987). Mankura et al. 1987 shown a rapid biotransformation into tissue lipids in fish (carp), for oleyl alcohol (C18, unsaturated). Bioaccumulation of fatty alcohol is unlikely in fish.
To conclude, the rapid degradation , the various metabolic pathways and excretion routes which can be expected for the substance, shown that the bioaccumulation of the substance is unlikely.
References:
Mitsumasa Mankura and Mitsu Kayama. Wax Ester Synthesis by Carp Hepatopancreas Preparation, 1986. Journal of Japan Oil Chemists' Society Vol. 36, No. 4, 244-253.
Mitsumasa Mankura, Noriaki Iijima, Mitsu Kayama and Satoshi Aida. Plasma Transport form and Metabolism of Dietary Fatty Alcohol and Wax Ester in Carp, 1987. Nippon Suisan Gakkaishi 53(7), 1221-1230.
Key value for chemical safety assessment
Additional information
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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