Registration Dossier
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EC number: 700-486-0 | CAS number: 102687-65-0
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
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- Density
- Particle size distribution (Granulometry)
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- Endpoint summary
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- Transport and distribution
- Environmental data
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- 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
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- Biotransformation and kinetics
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- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
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- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
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- Specific investigations
- Exposure related observations in humans
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- Additional toxicological data

Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
The short-term toxicity of the substance to aquatic invertebrates was determined in a study in accordance with OECD TG 202. In this study the 48-h EC50 was determined at 82 mg/L (measured concentration).
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 82 mg/L
Additional information
The short-term toxicity of the substance to aquatic invertebrates was determined in a study in accordance with OECD TG 202 and in compliance with GLP criteria (Brixham Envriomental laboratory, 2010). In this study, Daphnia magna (4 replicates of 5 animals per concentration) were exposed to nominal concentrations of 0, 4.38, 8.75, 17.5, 35 and 70% of saturation for 48 hours under static conditions. Nominal concentrations were prepared by bubbling test substance through 3500 mL of media for approximately 60 minutes to obtain a saturated solution of the gas (100 %). This was then diluted to 70 % saturation with media that had been diffused with oxygen for 30 minutes. All other concentrations were prepared from the 70 % stock. Test concentrations were analytical verified. Mean measured concentrations were 27, 38, 91, 175 and 405 mg/L. After 48 hours exposure, an effect was first seen at 38 mg/L with 5% immobilisation. At 91 and 175 mg/L, immobilisation percentages were 65 and 95%, respectively and at the highest concentration tested all Daphnia were immobilised. Based on these findings, the 48 -h EC50 was determined at 82 mg/L (measured concentration).
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