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EC number: 225-716-2 | CAS number: 5026-74-4
- 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
Based on the substances similarities of the physical and chemical properties and ecotoxicological profile to m-(2,3-epoxypropoxy)-N,N-bis(2,3-epoxypropyl)aniline, a read across has been proposed to fullfil toxicological endpoints where no data is available on the target substance. Please see the relevant endpoint summaries and read across justification document enclosed in Chapter 13.
Short term toxicity from three trophic levels (Daphnia, Fish and Algae) is available for the misomer and for two trophic levels (Fish and Algae) for the p-isomer substance. The results showed that L(E)C50 values to Fish and Algae are very similar (>4.2 mg/L to 5.4 mg/L for Fish and 13 mg/L to 18 mg/L for Algae). Additionally, a chronic study on daphnia reproduction is available on the p-isomer.
Based on the results mentioned above on physico-chemical properties and environmental fate and given that short term toxicity on Fish and Algae species are very similar, it is highly likely that the p-isomer substance will show the same acute toxicity to aquatic invertebrate than the m-isomer and that the m-isomer will have the same chronic toxicity to Daphnia Magna in a reproduction test than the p-isomer. Consequently, we consider scientifically justified to read-across from the m-isomer to the p-isomer and vice versa. For further information, please refer to the read across justification document enclosed in chapter 13.
Additional information
Available Data for
p-(2,3-epoxypropoxy)-N,N-bis(2,3-epoxypropyl)aniline
In the short-term toxicity study on Carp, the LC50 after 96 hours of treatment was 4.2 mg/L with 0% mortality at 3.2 mg/L and 100% mortality at 5.6 mg/L.
In the short-term toxicity study on Daphnia magna, the test substance did not induce significant acute immobilisation of Daphnia magna at 10 mg/L after 48 hours of exposure based on analytically confirmed nominal exposure concentrations. The 48h-EC50 was 18 mg/L based on analytically confirmed nominal exposure concentrations (95% confidence interval between 10 and 32 mg/L)
In the long-term toxicity study on Daphnia magnia, the exposure to the concentrations of 1.7 mg/l and higher induced significant inhibition of the reproductive capacity of the parental daphnids (LOEC for reproduction). The 21d-EC50 for reproduction was 1.4 mg/l and the 21d-NOEC value for reproduction was 0.42 mg/l.
In the toxicity study to fresh water algae on Pseudokirchneriella subcapitata, the substance reduced significantly the growth rate of the algae species at an average exposure concentration of 26 mg/l. The EC50 for growth rate reduction was 13 mg/l, the EC50 for yield inhibition was 7.0 mg/l and the NOEC for growth rate reduction was 4.2 mg/l, while NOEC for yield inhibition could only be estimated to be < 2.5 mg/l.
Toxicity to microorganisms, investigated on Pseudomonas putida led to no inhibition of the growth rate. The EC10 and EC50 values were > 10 000 µg/L.
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