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EC number: 908-381-3 | CAS number: -
- 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
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Not GLP but well documented
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Principles of method if other than guideline:
- Preliminary tests
An amount of 100 mg of the test substance was magnetically stirred with 100 ml of milliQ water for 24 hours at ambient temperature (23 ± 1 °C). After subsequent centrifugation of the solution, an insoluble fraction was observed. The test was repeated with 10 mg, instead of 100 mg, of test substance in 100 ml of milliQ water. In this case, the dissolution was complete. In the preliminary tests, the water solubility of the test substance was > 0.01 g/l. Therefore, the flask method was chosen for the main test.
Main test
Three aliquots of 250 mg of the test substance were weighed into three flasks. To each flask, 50 ml of milliQ water were added. The solutions were magnetically stirred in a thermostatic bath at 30 °C for 24, 48 or 72 hours. As a blank, 50 ml of milliQ water were stirred for 48 hours. After stirring, the solution was re-equilibrated for 24 hours in a thermostatic bath at 20 ±1 °C with occasional manual shaking. The solution was then centrifuged at ambient temperature during 5 min at 4 000 rpm. A pH measurement was performed on the soluble phase.
Because the test sample is a mixture, no specific analytical method was used to determine the solubility. Two aliquots of 20 ml of the soluble phase were dried in two steps: after a first period of evaporation at 60-70 °C under nitrogen, the residues were placed in a vacuum oven at 60 °C until constant weight. - GLP compliance:
- no
- Type of method:
- flask method
Test material
Reference
- Name:
- Unnamed
- Type:
- Constituent
- Details on test material:
- Two samples of the test substance were tested: SOLVCAT and Granelli CRG
Both were sampled on 2 September 2009
Results and discussion
Water solubility
- Water solubility:
- >= 2.9 - <= 3.1 g/L
- Temp.:
- 20 °C
- pH:
- >= 7.5 - <= 8.5
Any other information on results incl. tables
The solubility results (individual and mean values) and pH measurements are summarized in the table below for the Solvcat sample. The solubility measured for the blank was < 0.1 g/l.
Stirring time (hours) |
Solubility (g/l) trial 1 |
Solubility (g/l) trial 2 |
Solubility (g/l) mean value |
pH |
24 |
3.1 |
3.1 |
3.1 |
8.0 – 8.5 |
48 |
3.1 |
3.1 |
3.1 |
8.0 – 8.5 |
72 |
3.1 |
3.1 |
3.1 |
8.0 – 8.5 |
No difference is observed between the individual results, the water solubility of the test substance is 3.1 g/l.
The solubility results (individual and mean values) and pH measurements are summarized in the table below for the Granelli CRG sample. The solubility measured for the blank was < 0.1 g/l.
Stirring time (hours) |
Solubility (g/l) trial 1 |
Solubility (g/l) trial 2 |
Solubility (g/l) mean value |
pH |
24 |
2.8 |
2.9 |
2.9 |
7.5 – 8.0 |
48 |
2.9 |
2.9 |
2.9 |
7.5 – 8.0 |
72 |
2.9 |
2.9 |
2.9 |
7.5 – 8.0 |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): soluble (1000-10000 mg/L)
Based on the experimental study, which used a nominal concentration of 5 g/l, the water solubility of the substance is 2.9 - 3.1 g/l. However, it should be realised that the constituents sodium chloride (>100 g/l) and calcium sulfate (2.4 g/l) have a high water solubility, while calcium carbonate and magnesium hydroxide have a low water solubility (< 100 mg/l). When the experimental study would have been started with a higher nominal concentration most likely a higher water solubility would have been obtained (a higher amount of calcium sulfate and sodium chloride could dissolve).
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