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EC number: 619-447-3 | CAS number: 99607-70-2
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
In order to evaluate the short-term effect of cloquintocet-mexyl to aquatic invertebrates, two guideline studies were conducted with Daphnia magna. In both cases, no significant effects were observed. Therefore, the EC50 value of 100 mg/L, which corresponds to the highest concentration tested, is used for risk assessment purposes.
In the case of the metabolite CGA153433, the 48-hour EC50 for Daphnia magna was determined to be > 9.7 mg/L.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 100 mg/L
Additional information
In the key study (Rufli, 1988), 2 groups of 10 daphnids (Daphnia magna) were exposed to cloquintocet-mexyl at nominal concentrations of 10, 18, 32, 58 and 100 mg/L, in a static test for 48 hours. The 48-hour EC50 forD. Magna was >100 mg/L, the highest concentration tested. The no observed effect concentration was 18 mg/L. This GLP-compliant study was conducted to EPA guideline EG-1 and was considered to be reliable without restrictions.
In a second study (Palmer and Krueger, 1998), daphnids (Daphnia magna) were exposed to cloquintocet-mexyl at nominal concentrations of 0.063, 0.13, 0.25, 0.50 and 1.0 mg/L, in a flow-through test for 48 hours. The 48-hour EC50 forD. magna was > 0.82 mg/L, the highest (measured) concentration tested. The no observed effect concentration was 0.82 mg/L. This GLP-compliant study was conducted to OECD guideline 202 and was considered to be reliable without restrictions.
Since both studies indicate that the EC50 is greater than the concentrations tested, it is proposed to select the upper of the two test rates as the key value for the endpoint. Therefore, for risk assessment purposes, the EC50 of 100 mg/L was used for cloquintocet-mexyl.
A study of short-term toxicity of a metabolite of cloquintocet-mexyl, CGA153433, to D. magna was carried out (Putt, 1993). This GLP-compliant study was performed to OECD guideline 202 and is considered to be reliable without restrictions. Daphnids were exposed to a nominal concentration of 9.7 mg/L, in a semi-static system. No effects were observed at the test concentration, thus the 48-hour EC50 of the metabolite CGA153433 was determined to be > 9.7 mg/L.
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