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EC number: 213-607-2 | CAS number: 993-13-5
- 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)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- secondary literature
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- No details on materials and methods provided
- GLP compliance:
- not specified
- Analytical monitoring:
- not specified
- Vehicle:
- not specified
- Test type:
- not specified
- Water media type:
- not specified
- Duration:
- 14 d
- Dose descriptor:
- EC50
- Effect conc.:
- 17.805 mg/L
- Conclusions:
- Th 14d EC50 was reported to be 17.805 mg/L.
Reference
Description of key information
Acute toxicity for freshwater algae Pseudokirchneriella subcapitata (growth rate):
72h-EC50 = 43.1 mg MPAAU/L
72h-EC10 = 13.5 mg MPAAU/L
72h-NOEC = 3.2 mg MPAAU /L
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 43.1 mg/L
- EC10 or NOEC for freshwater algae:
- 13.5 mg/L
Additional information
A valid algal growth inhibition study (Kley 2012) with read across substance MPAAU revealed following results for growth rate: 72h-EC50 = 43.1 mg/L, 72h-EC10 = 13.5 mg/L, 72h-NOEC value = 3.2 mg/L. The algae therefore has been to be the most sensitive of the tested freshwater organisms.
The algal growth inhibition study of Williams 1987 was conducted with the target substance itself. However, the review article of Munro et al. (1999) is giving no further information than the mere result. But these data only are known from this single secondary literature source, it is furthermore not possible to verify the correctness of the data by a second independent data source. Because of this, further attempts were undertaken to retrieve the original study report from U.S. military web services (USCEHR, NTIS), but unfortunately without success. With no further clarification on data reliability possible, this renders the reliability of the acute algal growth inhibition study of Williams (1987) as not assignable (Klimisch 4).
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