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EC number: 201-167-4 | CAS number: 79-01-6
- 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:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: GLP status unknown, guideline study, published in peer reviewed literature, adequate for assessment.
- Qualifier:
- according to guideline
- Guideline:
- other: EPA-660/3-75-009
- Deviations:
- no
- GLP compliance:
- not specified
- Analytical monitoring:
- yes
- Details on sampling:
- A 100 mL water sample was collected and placed in a modified 100 mL volumetric flask. Each aquarium sampled at least 3 times to determine concentration.
- Vehicle:
- yes
- Details on test solutions:
- Acetone used as co-solvent to introduce chemicals into the diluter. Nominal acetone concentrations were 79-198 mg/l depending on diluter cell; measured concentrations of acetone in test tanks did not exceed 2% of LC50 for acetone (8,500 mg/l).
- Test organisms (species):
- Jordanella floridae
- Details on test organisms:
- Laboratory-reared juvenile (2-4 month old) fish were used. Fish were raised in the dilutent water and fed freshly-hatched and adult brine shrimp.
- Test type:
- flow-through
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Post exposure observation period:
- None
- Hardness:
- 48 mg/l as CaCO3
- Test temperature:
- 25±2°C
- pH:
- 6.95 ± 0.35
- Dissolved oxygen:
- >90%
- Salinity:
- Not applicable
- Nominal and measured concentrations:
- 5 or 6 duplicate concentrations in logarithmic series,
- Details on test conditions:
- Dechlorinated Lake Superior water taken from the Thunder Bay was used.
Fish were not fed during the test.
Water and acetone (79-198 mg/l) controls were employed.
No aeration was used during the test.
30 litre aquaria, 10 fish per aquarium, flow rate 6 litres/hour - Reference substance (positive control):
- not specified
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 28.3 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Non-GLP, non-guideline study, adequate for assessment
- Principles of method if other than guideline:
- 96h LC50 was determined by the method of Doudoroff et. al. (1951)
- GLP compliance:
- no
- Analytical monitoring:
- yes
- Vehicle:
- not specified
- Details on test solutions:
- solutions not aerated
- Test organisms (species):
- Limanda limanda
- Details on test organisms:
- 5 dab (Limanda limanda, marine fish) used, 15-20 cm long
- Test type:
- flow-through
- Water media type:
- saltwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Nominal and measured concentrations:
- Measured concentrations
- Details on test conditions:
- glass flow-through apparatus
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 16 mg/L
Referenceopen allclose all
Description of key information
The lowest acute toxicity value for freshwater fish was the 96h LC50 for American flagfish, Jordanella floridae which was 28.3 mg/l.
For marine water fish the lowest toxicity value was the 96h LC50 16 mg/l found in Limanda limanda.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 28.3 mg/L
Marine water fish
Marine water fish
- Effect concentration:
- 16 mg/L
Additional information
Several studies with both freshwater and marine fish are available. For the freshwater compartment a flow-through study with the American flagfish Jordanella floridae, conducted according to the EPA-660/3-75-00 guideline was found to be the most critical (Smithet al.1991). The 96-h LC50 was 28.3 mg/l. For the marine compartment a flow-through study with the dabLimanda limanda, was found to be most critical (Pearsonet al.1975). Although this study was not conducted according to an accepted guideline the study was a well conducted near-guideline study, the 96-h LC50 was 16 mg/l. Other studies were less critical and/or not reliable.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

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