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EC number: 696-364-9 | CAS number: 133779-11-0
- 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
Biodegradation screening tests are available for various structurally related alkyl-1,3-diaminopropanes. All alkyl-1,3-diaminopropanes under consideration consist of carbon, hydrogen and nitrogen only. The basic structure of all alkyl-1,3-diaminopropanes consists of a hydrocarbon chain with a 1,3-propanediamine group at the end of the chain. The only difference consists of differing chain lengths and slight variations in the degree of saturation in the alkyl chain. Since the majority of the alkyl chains consist of C12to C18units, and the unsaturated part is mainly located in the more central part of the alkyl chain, significant changes in chemical behavior and/or reactivity is not to be expected. Therefore the experimental data available for this group of alkyl-1,3 -diamines are used for the evaluation of the biodegradability of N-C12 -14–propane-1,3-diamine.
Based on the available studies on biodegradation, all alkyl 1,3 -diaminopropanes (C10 - C18) are considered to be readily biodegradable. The 10-days-window criterion does not need to be evaluated as the alkyl 1,3 -diaminopropanes are UVCB substances. No simulation tests for degradation rates under environmental conditions are available, therefore the default values suggested in the REACH guidance may be used. Because of the observed ready biodegradability there is no requirement for performing a soil biodegradation test (Annex IX. 9.2.1.3).However a soil biodegradation test is performed with the structurally related14C hexadecyl amine. The observed half-life of 14C hexadecylamine of 8.98 days at 20 °C as determined according to an OECD 307 test is used for read-across to the diamines as both the primary alkyl amines and diamines are structurally related, readily biodegradable and have a similar sorption to soil. This means that for the risk assessment a half-life for soil and sediment of 17 d at 12°C are considered realistic for diamines.
A waste water treatment simulation test was performed with amines, N-C16-18-alkyl (even-numbered) propane-1,3-diamine (133779-11-0). 99.4% removal was observed using specific chemical analyses (LCMS/MS) of the effluent during day 56 to 60 (n=5). In addition, sorption to sludge was measured and this accounted for 4.1% of the total removal which means that 95.3% was removed by biodegradation.
Summary table of degradation rate constants in various (eco) systems based on the ready biodegradability of alkyl-1,3-diaminopropanes:
(Eco)system |
Method |
Half-life |
Surface water (fresh) |
TGD default value for readily biodegradable substances |
15 days |
Surface water (fresh) sediment |
Read across from half-life hexadecylamine |
17 days |
Marine water |
TGD default value for readily biodegradabl substances |
50 days |
Soils |
Read across from half-life hexadecylamine |
17 daysa |
Degradation in sewage treatment plants |
Determined in STP simulation test |
99.4% removal primarily by biodegradation |
aHalf-life of the fraction dissolved in the water phase is expected to in the order of a few days.
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