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EC number: 603-837-5 | CAS number: 134605-64-4
- 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)
Description of key information
Freshwater: 96 hour LC50 3.9 mg a.i./L, Oncorhynchus mykiss, EPA OPP 72-1, EPA 540/9-85-006, ASTM Standard E729-88a, Drottar & Swigert 1996a
Saltwater: 96 hour LC50 4.6 mg a.i./L, Cyprinidon variegatus, EPA OPP 72-3, EPA 540/9-85-009 and ASTM E729-88a, Roberts & Swigert 1996
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 3.9 mg/L
Marine water fish
Marine water fish
- Effect concentration:
- 4.6 mg/L
Additional information
Two studies have been provided to address short term toxicity to fish in freshwater and one study to address acute toxicity in marine water.
Drottar & Swigert (1996a) and Drottar & Swigert (1996b) determined the 96 hour LC50 for the test material in the freshwater species Oncorhynchus mykiss and Lepomis macrochirus respectively. Both studies were performed in freshwater under flow-through conditions. The analytical confirmed concentrations ranged from 1.5 to 8.3 mg a.i./L in the first study and from 1.4 to 9.3 mg a.i./L in the second study. O. mykiss was shown to be the more sensitive species with a LC50 value of 3.9 mg a.i./L, whereas the LC50 was determined to be greater than the highest concentration tested for L. macrochirus, > 9.3 mg a.i./L.. Based on mortality and clinical signs of toxicity the NOEC was considered to be 2.5 mg a.i./L for O. mykiss and 3.6 mg a.i./L for L. macrochirus respectively. As O. mykiss is the standard species, and the results from this study are more worst case, this study has been considered to be the key study for freshwater fish and the LC50 value from this study of 3.9 mg a.i./L has been taken forward for risk assessment.
The short-term toxicity to marine fish was determined in an acute toxicity study performed on Cyprinodon variegates, in line with GLP and in accordance with the standardised guidelines EPA OPP 72-3, EPA 540/9-85-090 and ASTM E729-88a. Organisms were exposed to the test material at measured concentrations of 0.96, 1.5, 2.6, 3.9 and 4.6 mg a.i./L under flow-through saltwater conditions for 96 hours. Under the conditions of the test mortality was observed at concentrations ≥ 3.9 mg a.i./L. By termination mortality had reached 5% and 50% in the 3.9 and 4.6 mg a.i./L exposure groups, respectively. Clinical and behaviour observations were noted at concentrations ≥ 3.9 mg a.i./L including surfacing and spotted discolouration. Based on these observation the 96 hour LC50was determined to be 4.6 mg a.i./L with 95% confidence limits of 4.4 and 5.1mg a.i./L. The NOEC were determined to be 2.6 mg a.i./L. The study is considered to be reliable, relevant and adequate for risk assessment purposes.
All studies were performed to a high standard, in line with GLP and in accordance with standardised guidelines. They have thus been assigned a reliability score of 1 in line with the principles for assessing data quality set out in Klimisch (1997). The available data are deemed to be relevant, reliable and adequate for the purposes of risk assessment.
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