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EC number: 203-431-4 | CAS number: 106-79-6
- 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
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Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
The effect of the test item on the growth of Pseudokirchneriella subcapitata has been investigated according to OECD 201 guideline over a 72-Hour period and gave the following results based on the time-weighted mean measured test concentrations:
Inhibition of Growth Rate
ErC10 (0 - 72 h) : 0.49 mg/L
ErC50 (0 - 72 h) : 1.5 mg/L
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 1.5 mg/L
- EC10 or NOEC for freshwater algae:
- 0.49 mg/L
Additional information
A study was performed to assess the effect of the test item on the growth of the green alga Pseudokirchneriella subcapitata. The method followed was designed to be compatible with the OECD Guidelines for Testing of Chemicals (2006) No 201, "Freshwater Alga and Cyanobacteria, Growth Inhibition Test" referenced as Method C.3 of Commission Regulation (EC) No 761/2009.
Following a preliminary range-finding test, Pseudokirchneriella subcapitata was exposed to an aqueous solution of the test item at concentrations of 1.0, 3.2, 10, 32 and 100 mg/L (three replicate flasks per concentration) for 72 hours, under constant illumination and shaking at a temperature of 24 ± 1 °C. Samples of the algal populations were removed daily and cell concentrations determined for each control and treatment group, using a Coulter®Multisizer Particle Counter.
Chemical analysis of the test preparations at 0 hours showed measured test concentrations to range from 86% to 94% of nominal. Given that chemical analysis of the range-finding test preparations had shown a decline in measured test concentration occurred over the test period, additional test samples were prepared at 0 hours and incubated alongside the test to provide samples for analysis at 24 and 48 hours. Analysis of the test preparations at 24 hours showed measured test concentrations to range from less than the limit of quantitation (LOQ) of the analytical method employed (which was determined to be 0.0049 mg/L) at 1.0 mg/L through to 104% of nominal at 100 mg/L. Measured concentrations in the range of less than the LOQ at 1.0, 3.2 and 10 mg/L through to 87% of nominal at 100 mg/L were observed at 48 hours whilst concentrations in the range of less than the LOQ at 1.0, 3.2, 10 and 32 mg/L through to 26% of nominal at 100 mg/L were observed at 72 hours
Given this decline in measured test concentrations it was considered justifiable to base the results on the time-weighted mean measured test concentrations in order to give a "worst case" analysis of the data. Exposure of Pseudokirchneriella subcapitata to the test item gave the following results based on the time-weighted mean measured test concentrations:
Inhibition of Growth Rate
ErC10(0 - 72 h) : 0.49 mg/L
ErC20(0 - 72 h) : 0.71 mg/L
ErC50(0 - 72 h) : 1.5 mg/L
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