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EC number: 246-619-1 | CAS number: 25103-58-6
- 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 aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
The results of the key study (CERI, 2000) show there is no effect within 48h on Daphnia magna at concentrations greater than the solubility limit (0.056 to 0.0165 mg/L). For other studies used as supporting evidence similar results were found that support the evidence that little adverse effect is observed up to the limit of solubility.
Key value for chemical safety assessment
Additional information
The key study (CERI, 2000) was a GLP study following EU method C2 where daphnids were exposed to the substance in DMSO. The study was performed open but concentrations were measured and therefore the study is considered reliable and suitable for use. Effects were measured only at the highest concentration of 0.1 mg/L nominal. In the second highest concentration of 0.056 mg/L nominal measured at 0.0165 at test start to 0.00546 mg/L at test end) no effects were observed.
(Thiebaud, 1997) is a static GLP study following EU method C2 but as the analytical method was too insensitive to determine the concentrations used the study cannot be considered valid but is included as supporting evidence.
Cowgill performed a supporting study documented in a publication detailing a semi-static study on Ceriodaphnia, following a method similar to that of OECD guideline 202. The report is detailed and the study follows standard scientific practices but as it was conducted in an open system without analysis it cannot be considered reliable. The DOW (1990) study is an open, static, 48 hour study with reference substance, following standard US EPA methods. However, this can only be used as a supporting study as the acetone vehicle was above OECD guideline limits (500 µL/L), no analysis was performed and all nominal concentrations of tert-dodecanethiol were above the water solubility limit. The Jenkins (1990) study was a static, 48 hour test on Daphnia magna. It did not follow OECD guidelines, but was conducted according to a study protocol (PTS9). No analytics were included and effects occurred only at concentrations nominally far greater than the solubility limit.
Three further endpoint values were located from other studies and these are documented in the review by Thomas & Comber (2013). Only the 24 h EC50s were determined and all values were >0.25 mg/L but insufficient information was available to prepare an endpoint summary and they have not been included in the IUCLID.
Based on the above information it can be concluded that none of the studies resulted in an EC50 at less than or at the water solubility limit of the substance.
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.
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