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EC number: 949-859-1 | CAS number: -
- 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
Fresh water algae study, 72 Hours, ERC10 = 0.24 mg/L, ERC50 = 1.2 mg/L, NOEC = 0.13 mg/L.
This 72h-ErC50 value for the substance based on the di-ester (1.2 mg/L) represents a Water Soluble Fraction prepared at a loading rate of 10 mg/L and this 72h-ErC10 value for the substance based on the di-ester (0.24 mg/L) represents a Water Soluble Fraction prepared at a loading rate between 1 and 3.2 mg/L.
Key value for chemical safety assessment
Additional information
A 72 hour toxicity study with freshwater algae (Pseudokirchneriella subcapitata ) was conducted according to OECD guideline 201 and GLP principles.
The algae were exposed toWSFs individually prepared at loading rates of 1.0, 3.2, 10 and 32 mg/L,and solutions containing 10 and 32% of the WSF prepared at a loading rate of 1.0 mg/L.
Samples taken from all test concentrations and the control were analysed by following the mono-ester (m/z 209.1) and di-ester (m/z 321.1).The measured concentrations of the mono-ester were 0.092, 0.32, 0.98, 3.3, 9.9 and 32 mg/L at the start of the test, respectively to the 10 and 32% dilutions of the 1.0 mg/L WSF and the loading rates of 1.0, 3.2, 10 and 32 mg/L. The concentrations remained generally stable, i.e. the 1.0 to 32 mg/L WSFs were at 82-94% relative to initial at the end of the test, however the 10 and 32% dilutions of the 1.0 mg/L WSF decreased to 72-73% of initial at the end of the test.
The measured concentrations of the di-ester were 0.010, 0.039, 0.13, 0.40, 1.2 and 3.4 mg/L at the start of the test, respectively to the 10 and 32% dilutions of the 1.0 mg/L WSF and the loading rates of 1.0, 3.2, 10 and 32 mg/L. The concentrations remained stable, i.e. were at 100-111% relative to initial at the end of the test.
Based on these results, effect parameters were expressed as initially measured concentrations of the di-ester, since the lower measured concentrations represent the worst case scenario.
The substance inhibited growth rate of this freshwater algae species significantly at measured concentrations of 0.40 mg/L and higher.The 72h-EC50 for growth rate inhibition (ERC50) was 1.2 mg/L with a 95% confidence interval ranging from 1.1 to 1.4 mg/L. The 72h-NOEC for growth rate inhibition was 0.13 mg/L. The 72h-EC10 for growth rate inhibition was 0.24 mg/L.
This 72h-ErC50 value for the substance based on the di-ester (1.2 mg/L) represents a Water Soluble Fraction prepared at a loading rate of 10 mg/L and this 72h-ErC10 value for the substance based on the di-ester (0.24 mg/L) represents a Water Soluble Fraction prepared at a loading rate between 1 and 3.2 mg/L.
The study met the acceptability criteria, and is considered to be valid.
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