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EC number: 261-245-9 | CAS number: 58430-94-7
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
The growth rate of freshwater green algae exposed to the substance was inhibited. The 72-hour and 96-hour ErC50 values were greater than the highest concentration that could be maintained under test conditions (3.8 mg/L). The ErC10 after 72-hours was 0.65 mg/L (mean measured).
Key value for chemical safety assessment
- EC10 or NOEC for freshwater algae:
- 0.65 mg/L
Additional information
The effects of the test item 3,5,5-trimethylhexyl acetate on the growth of the freshwater green alga Pseudokirchneriella subcapitata were examined after 72 and 96 hours of exposure in a closed test system, according to OECD TG 201, EC No. L383 Method C.3 and OCSPP Number 850.4500.
Nominal concentrations were 1.0, 2.6, 6.4, 16 and 40 mg/L. All test solutions appeared clear and colorless and were otherwise unremarkable at test initiation. At test termination, there were no visible particulates or surface-slicks in any of the test chambers. Results of the study were based on geometric mean, measured test concentrations, calculated using the measured concentrations at 0, 24, 48, 72 and 96 hours of exposure, of 0.51, 1.2, 1.9, 3.0 and 3.8 mg/L, equivalent to 51, 46, 30, 19 and 10 % of nominal concentrations, respectively. The controls showed that the substance may adhere to the algae.
The toxicity of 3,5,5-trimethylhexyl acetate to P. subcapitata was determined by evaluating changes in cell density over a 72- and 96-hour exposure period. Cell densities of algae in exponential growth phase were used to determine area under the growth curve, growth rates and yield at 72 and 96 hours of exposure.
The 72-hour ErC50 value for growth rate was >3.8 mg/L. Reductions in area under the growth curve, growth rate and yield were statistically significant (Dunnett’s test; p < 0.05) in all treatment groups at 72 hours of exposure. The 72-hour NOEC was determined to be < 0.51 mg/L.
The 72 and 96-hour ErC10 values for growth rate were calculated as 0.65 and 3.3 mg/L, respectively.
After 96 hours of exposure, the ErC50 value for growth rate was >3.8 mg/L. Area under the growth curve was significantly reduced (Dunnett’s test; p < 0.05) in all treatment groups at 96 hours of exposure. The 96-hour NOEC was determined to be < 0.51 mg/L.
After 96 hours of exposure, there were no signs of noticeable aggregation or flocculation of cells in the negative or solvent control groups or in any treatment groups. Cells were not observed to be adhering to the test vessels in any of the experimental groups. P. subcapitata cells in the treatment levels and the solvent control appeared normal when compared to cells present in the negative control.
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