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EC number: 813-338-6 | CAS number: 106155-02-6
- 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
Water solubility
Administrative data
Link to relevant study record(s)
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- from 12th of April, 2016 to 9th of May, 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Version / remarks:
- OECD Guidelines for the Testing of Chemicals, Method No. 105, adopted 27. Jul. 1995: “Water Solubility"
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Version / remarks:
- Council Regulation (EC) No 440/2008 of 31. May 2008, Method A.6: “Water solubility” (last updated by Reg. 260/2014)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Key result
- Water solubility:
- 59.36 mg/L
- Conc. based on:
- test mat.
- Loading of aqueous phase:
- 1 g/L
- Incubation duration:
- 5 d
- Temp.:
- 20 °C
- pH:
- 6
- Key result
- Water solubility:
- 0.059 kg/m³
- Conc. based on:
- test mat.
- Loading of aqueous phase:
- 1 g/L
- Incubation duration:
- 5 d
- Temp.:
- 20 °C
- pH:
- 6
- Details on results:
- Findings and Results:
The solubility of the test item Sandalmysore Core in water was determined by measurement of the test item concentration in the centrifuged test solutions using HPLC-UV.
The solubility of the test item was estimated to be < 1 g/L in the solubility pre-test. According to the guideline, the flask method was used for the determination of the solubility of the test item in water.
A first experiment was not evaluable due to technical issues with the HPLC determination. However it indicated that the solubility is < 100 mg/L and not dependent on nominal load, therefore the loading rate 1 g/L was chosen for all flasks in experiment 2. Equilibrium was reached after 5 d.
No Tyndall effect (i.e. a laser beam was not scattered when transmitted through the liquid) could be observed indicating that no colloidal dispersed particles were present in centrifuged solutions.
At the plateau, the concentration of Sandalmysore Core in water had reached:
59.36 ± 3.29 mg/L at 20.0 ± 0.1 °C
5.936 ± 0.329 * 10-2 kg/m3 (SI units)
(mean value ± standard deviation of five independent determinations in five individual vessels) - Conclusions:
- Concentration of the test item in water:
59.36 ± 3.29 mg/L at 20.0 ± 0.1 °C
= 5.936 ± 0.329 * 10-2kg/m3 (SI units)
(mean value ± standard deviation of five independent determinations in five individual vessels) - Executive summary:
The solubility of the test item in water was determined by measurement of the test item concentration in the centrifuged test solutions using HPLC-UV according to OECD 105 resp. EU A.6
The solubility of the test item was estimated to be < 1 g/L in the solubility pre-test. According to the guideline, the flask method was used for the determination of the solubility of the test item in water.
A first experiment was not evaluable due to technical issues with the HPLC determination. However it indicated that the solubility is < 100 mg/L and not dependent on nominal load, therefore the loading rate 1 g/L was chosen for all flasks in experiment 2. Equilibrium was reached after 5 d.
No Tyndall effect (i.e. a laser beam was not scattered when transmitted through the liquid) could be observed indicating that no colloidal dispersed particles were present in centrifuged solutions.
At the plateau, the concentration of the test item in water reached
59.36 ± 3.29 mg/L at 20.0 ± 0.1 °C = 5.936 ± 0.329 * 10-2kg/m3 (SI units)
(mean value ± standard deviation of five independent determinations in five individual vessels)
Reference
Description of key information
The solubility of the test item in water was determined by measurement of the test item concentration in the centrifuged test solutions using HPLC-UV according to OECD 105 resp. EU A.6
The solubility of the test item was estimated to be < 1 g/L in the solubility pre-test. According to the guideline, the flask method was used for the determination of the solubility of the test item in water.
A first experiment was not evaluable due to technical issues with the HPLC determination. However it indicated that the solubility is < 100 mg/L and not dependent on nominal load, therefore the loading rate 1 g/L was chosen for all flasks in experiment 2. Equilibrium was reached after 5 d.
No Tyndall effect (i.e. a laser beam was not scattered when transmitted through the liquid) could be observed indicating that no colloidal dispersed particles were present in centrifuged solutions.
At the plateau, the concentration of the test item in water reached
59.36 ± 3.29 mg/L at 20.0 ± 0.1 °C = 5.936 ± 0.329 * 10-2 kg/m3 (SI units)
(mean value ± standard deviation of five independent determinations in five individual vessels)
Key value for chemical safety assessment
- Water solubility:
- 59.36 mg/L
- at the temperature of:
- 20 °C
Additional information
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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