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Diss Factsheets
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EC number: 200-882-9 | CAS number: 75-59-2
- 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
There are two studies available. In the key study, the nominal 72h-ErC50 value and NOECr value to Pseudokirchnerella subcapitata were 96.3 and 6.25 mg/L, respectively.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 96.3 mg/L
- EC10 or NOEC for freshwater algae:
- 6.25 mg/L
Additional information
A toxicity test with Pseudokirchnerella subcapitata was carried out by the TMAH Consortium (2005) according to OECD 201 and GLP under static conditions. Analytical monitoring was conducted. The TMAH concentrations in test solutions were maintained within ± 20% of nominal concentrations throughout the test. Thus the value was estimated with nominal concentrations. The nominal 72h-ErC50 value and NOECr value were 96.3 and 6.25 mg/L, respectively.
A toxicity test with Desmodesmus subspicatus was carried out by Scheerbaum (2001) in accordance with OECD 201, EU Method C.3 (Algal Inhibition test) and GLP. The nominal 72h-ErC50 value and NOECr value to Desmodesmussubspicatus were >251 and 31.4 mg/L, respectively.The recovery rates of samples taken at the start and the end of the test based on DOC measurements were > 80% and therefore it is deemed acceptable to express the results as nominal values. As no significant effects was observed in neutralised solution of 251 mg/L TMAOH (pH control), it can be concluded that the effects are pH dependent.
The study from TMAH Consortium (2005) was selected as a key study because the EC50 and NOEC values were lower. Probably Pseudokirchnerella subcapitata is more sensitive to TMAOH than Desmodesmus subspicatus. Furthermore, the nominal concentrations in the study from the TMAH Consortium (2005) were confirmed by specific analytical measurements, whereas in the study by Scheerbaum (2001) DOC measurements were carried out, which was a reason to assign a lower reliability to it.
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