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EC number: 268-215-4 | CAS number: 68037-92-3 This substance is identified by SDA Substance Name: C16-C22 alkyl amine and SDA Reporting Number: 21-029-00.
- 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
Stability
The hydrolysis test was waived in accordance with column 2 of Annex VIII of Regulation 1907/2006/EC as the substance was readily biodegradable.
Biodegradation
In a biodegradation study according to OECD TG 301D (GLP, reliability 1) 69% oxidation was found after 28 days. The study demonstrates that the substance is readily biodegradable.
Bioaccumulation
The BCF was estimated to 613 L/kg ww with Arnot&Gobas BCFBAF method. Together with the estimated log Kow of 5.4 this indicates that C16 -22 might have a bioaccumulation potential. However, it is well known that the BCF of polar substance like C16 -22 alkylamine is difficult to predict. Performance of a standard aquatic exposure based OECD 305 test is however not considered as the substance sorbs easily to negatively charged surfaces like glassware, clay etc. and the substance will also biodegrade. Standard OECD 305 tests are therefore technically not feasible with these strongly sorbing degradable substances. In addition is the route of exposure unrealistic because the substance will either be sorbed or biodegraded in a natural environment.
For this reason and also for ethical reasons it would be better to evaluate if the substance is metabolized by an hepatic S9 fraction of rainbow trout. At the moment the substance is metabolized, the chance of accumulation of C16 -22 akylamine in fish is considered to be small (WOE-approach). The bioaccumulation potential of the C16-22 alkylamine is considered to be significantly lower than predicted based on the calculated Log Kow. This is because biotransformation of the C16-22 primary alkyl amines is considered to be very likely, as biotransformation has been observed for the C16 constituent (Perdu-Durand et al 2006). As the C16 -22 alkylamine is readily biodegradable it is also unlikely that the substance will accumulate in the food chain.
In conclusion the Arnot&Gobas BCFBAF estimation method, the biodegradation profile and the observed biotransformation of the C16 constituent indicate that the substance in not bioaccumulative despite having a log Kow >4.5.
Transport and distribution
The adsorption desorption was started but shown to be non feasible for this substance as described in section 5.4.1 of this dossier. Instead, a Log Koc was calculated as a weighted average based on data from US KOWWIN for respectively average of the ionic amine R‐NH3+ and neutral amine R‐NH2 constituents. The calculated Log Koc was 4.61.
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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