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EC number: 939-238-3 | 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
A reliable toxicity study to aquatic algae and cyanobacteria (reliability 2) with read-across substance Isostearic acid, esters with methyl α-D-glucoside is available. The NOEC of 100 mg/L, which was above the solubility limit of the test substance and 72 h-ErC50 of > 100 mg/L (nominal) were determined in a study performed according to OECD guideline 201.
Key value for chemical safety assessment
- EC10 or NOEC for freshwater algae:
- 100 mg/L
Additional information
Based on the structural analogue approach to Stearic acid, esters with methyl α-D-glucoside read across from Isostearic acid, esters with methyl α-D-glucoside is considered acceptable.
The structural analogue approach is scientifically justified by close similarities with regard to structural aspects and physico-chemical, environmental toxicological as well as toxicological properties.
With regard to Physical and chemical properties this approach is based on meting and boiling tests, vapour pressure studies and water solubility studies. Similar environmental toxicological properties were observed in standard biodegradation studies and studies on toxicity to microorganisms. Furthermore, comparable data on Acute Oral Toxicity in rats can be considered.
Toxicity to aquatic algae and cyanobacteria
In a 72 h acute toxicity study according to OECD guideline 201, the cultures of Pseudokirchnerella subcapitata NIVA CHL 1 were exposed to Isostearic acid, esters with methyl α-D-glucoside at a nominal concentration of 100 mg/L under static conditions in accordance to OECD Guideline 201. No analytical control was performed, and the test substance could not be completely dissolved in test medium at the loading rate tested.
The NOEC value was 100 mg/L, which was above the solubility limit of the test substance. 72 h-ErC50 for growth inhibition rate and the 72 h-EyC50 for yield inhibition exceeded the maximum input concentration of 100 mg/L of the test substance. The % growth inhibition in the treated algal culture compared to the control was slightly reduced (8.5%). The reduction was not considered to be of biological significance, as it was less than 10%. The total yield was inhibited by 36% when compared to the control. Hence, a 50% effect level could not be reached at the maximum input concentration of the test substance.
There were no abnormalities noted.
Results Synopsis
Test Organism: Pseudokirchnerella subcapitata NIVA CHL 1
Test Type: static
72 hr ErC50for growth rate: >100 mg/L (nominal)
72 hr EyC50for yield: >100 mg/L (nominal)
72 hr NOEC for growth rate: 100 mg/L (nominal)
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