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EC number: 235-049-9 | CAS number: 12062-81-6
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: as reported in source record
- Justification for type of information:
- see attachment "Read-across justification-environ assessment-iron oxides" and “Endpoint-specific read-across justification for nano forms of iron oxide, 2021” attached in IUCLID section 13.
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- >= 100 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: as reported in source record
Reference
Description of key information
Applying read-across to nanosizediron(hydr)oxides (see attachment "Read-across justification-environ assessment-iron oxides" and “Endpoint-specific read-across justification for nano forms of iron oxide, 2021” attached in IUCLID section 13), nanosized iron manganese trioxide is not considered acutely toxic to fish. Respective 96-h LC50 values for the toxicity of nanosized iron (hydr)oxides to Danio rerio range from > 10,000 mg/L to > 100,000 mg/L, a concentration that is 1000-fold above the corresponding OECD test limit.
Key value for chemical safety assessment
Additional information
Acute toxicity of iron(hydr)oxidenanoforms was investigated in two reliable studies using nanosized diiron trioxide (Weyers, 1985) and iron hydroxide oxide yellow (Weyers & Caspers, 1989). Acute toxicity ofnano-alphadiiron trioxide was investigated under static conditions in accordance with the proposed procedure for lethal effect on Zebrabaerbling (Federal Environmental Agency Germany, May 1984) and an unbounded 96 h LC50 of > 10 g/L (nominal) was derived. Fornano-alphairon hydroxide oxide yellow within 96 hours no effects (LC0) on Danio rerio were observed up to a concentration of 100 g/L. The method used was a proposed procedure for lethal effect on Zebrabaerbling (Federal Environmental Agency Germany, May 1984).
Based on read-across to nanosized iron (hydr)oxides (see attachment "Read-across justification-environ assessment-iron oxides" and “Endpoint-specific read-across justification for nano forms of iron oxide, 2021” attached in IUCLID section 13), available data indicate a low potential for acute aquatic toxicity ofnanosized iron manganese trioxideto fish (see table below).Acute toxicity of nanosizediron (hydr)oxidesto fish was not observed up to 100 g/L (Weyers & Caspers, 1989), a concentration that is 1000-fold above the corresponding OECD test limit for acute toxicity.
Table: Acute aquatic toxicity of nanosized iron(hydr)oxidesto fish.
Endpoint |
Test species |
Test results |
Test material/form |
Reliability: Reference |
Short-term toxicity to fish |
Danio rerio |
LC50 (96h): > 10 g/L nominal LC0 (96h): >= 10 g/L nominal |
diiron trioxide / nano, alpha |
RL2: Weyers, 1985 |
. |
Danio rerio |
LC50 (96h): > 100 g/L nominal LC0 (96h): >= 100 g/L nominal |
iron hydroxide oxide yellow / nano, alpha |
RL2: Weyers & Caspers, 1989 |
Supportive information microsized iron (hydr)oxides
Respective 96-h LC50 values for the toxicity of microsized iron (hydr)oxides to Danio rerio range from > 10,000 mg/L to > 100,000 mg/L, a concentration that is 1000-fold above the corresponding OECD test limit.
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