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EC number: 629-765-4 | CAS number: 1226892-44-9
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
The toxicity to aquatic algae in a valid algae study resulted in a 72 hour EC10 and EC50 based on growth of resp. 323.8 and 476.7 µg a.i./L
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 476.7 µg/L
- EC10 or NOEC for freshwater algae:
- 323.8 µg/L
Additional information
Two algae toxicity studies have been performed. One study performed to assess the algae toxicity of a range of comparable imidazoline products and one definitive study with 1H-Imidazole-1-ethanamine, 4,5-dihydro-, 2-nortall-oil alkyl derivs. (CAS no 68442-97-7). The 72 h EC10 based on growth is 343 µg/L based on the nomimal test substance concentration. Corrected for active ingredient which is 94.4% the EC10 is reduced to 323.8 µg/L.. The test was performed with river water as it is intended to be used in an evaluation of the environmental risks based on the Bulk approach where it is essential to show that the organisms were fully exposed to the nominal test concentration. During the test a decrease of the concentration is observed of about 70%. Imidazolines are susceptible to hydrolysis and the decrease observed could therefore be assigned to either hydrolysis or sorption or both processes. Imidazolines will however only hydrolyze to an amidoamine which is relatively resistant to hydrolysis under ambient conditions. As this hydrolysis will also occur under environmental conditions and amidoamines have a comparable ecotoxicity as the imidazolines the nominal concentration based on active ingredient is considered as the concentration to be used for the dose effect assesment. No significant adsorption to glassware was observed and the organisms were thus fully exposed the the nominal concentration based on active ingredient. Initially to the imidazoline which might have slowly changed into an amidoamine during the test. It is considered realistic to relate the observed effects to the nominal values based on active ingredient.
The effects observed in the definitive study are in good agreement with the results observed in the first study.
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