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EC number: 682-872-8 | CAS number: 957787-76-7
- 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/Hydrolysis
Based on the hydrolysis as function of pH test (OECD guideline N°111), N,N'-bis(1,2,2-trimethylpropyl)-1,6-hexane diamine is considered as hydrolytically stable. Less than 10% hydrolysis occurred after 5 days when tested at pH 4, 7 and 9 at 50°C with an average initial concentration of 0.04 g/L. These results assessed by gas chromatography lead to half-life values greater than 1 year at 25°C.
Biodegradation
To assess the biodegradability of N,N'-bis(1,2,2-trimethylpropyl)-1,6-hexane diamine, the ready biodegradability test under aerobic conditions was performed (OECD guideline N°301B). After 28 days of exposure at 21°C, the test material attained 44% degradation after 28 days determined by measuring the carbon dioxide produced. In that context, the test substance is not considered as readily biodegradable. However, a degradation of 44% in a strignent ready test, indicates a potential for degradation in treatment plants that can be confirmed by a test on inherent biodegradability. In addition, the no ready biodegradability has also been supported through results given with BIOWIN3 AND BIOWIN5. The persistency status given by the results of BIOWIN2,6 and 3 were however at the borderline value leading to mixed results.
Bioaccumulation
According to the logKow determined by the shake-flask method, the substance (N,N'-bis(1,2,2-trimethylpropyl)-1,6-hexane diamine) does not have the property to bioaccumulate in living organisms (LogKow = 2.10).
Transport and distribution
Estimations of the logKoc indicate that N,N'-bis(1,2,2-trimethylpropyl)-1,6-hexane diamine can bind to solid surfaces. Indeed, log Koc estimate from KOCWIN v2.00 (US EPA, February 2009) gave a value of 4.47 which is in the same order of magnitude as the Koc estimate from the log Kow (log Koc = 4.06). The adsorption coefficient was not determined by HPLC due to the protonation of the amine groups at pH tested. At pH tested (5.5 -7.5), the amine groups are positively charged on the nitrogen which interacts with the column stationary phase by forces other than partitioning.
The Henry's law constant of 5.436 Pa.m3/mol determined by modeling (EPIWEB v4.1), demonstrates that the substance will not evaporate easly from the surface water.
In conclusion,
According data currently gathered on the substance, N,N'-bis(1,2,2-trimethylpropyl)-1,6-hexane diamine will adsorb on suspended matters or sediment in water, and will thus be removed from the water column to a certain extend reducing the direct toxicity of the test item to organisms remaining in the water column (fish, daphnia and algae). In soil, the substance is likely to remain adsorbed on soil particles and low losses are expected by run off to the groundwater.
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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