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EC number: 429-580-7 | 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
Link to relevant study record(s)
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2006-07-24 to 2006-08-14
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Version / remarks:
- 1992
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Version / remarks:
- 1995
- GLP compliance:
- yes
- Type of method:
- column elution method
- Key result
- Water solubility:
- < 0.042 mg/L
- Conc. based on:
- test mat.
- Incubation duration:
- 72 - 75 h
- Temp.:
- 25 °C
- pH:
- >= 5.7 - <= 6.9
- Details on results:
- Preliminary Visual Estimation of the Water Solubility
Increasing water amounts were added stepwise to different amounts of the test item. The preliminary visual experiments showed that the water solubility of the test item is below 10.7 mg/L. Therefore the water solubility had to be determined by the "column elution method". - Conclusions:
- The water solubility of the test item was determined to be < 0.042 mg/L at 20°C.
- Executive summary:
The water solubility was determined according to OECD 105 using the column elution method with HPLC analysis. Two identical samples were prepared, one of them was exposed to a flow rate of 12.5 mL/h (column 1), the other one to 25.0 mL/h (column 2). After measurement of the volume, pH and temperature, the fractions were subjected to HPLC analysis. For the determination of the water solubility it was not necessary to combine or to concentrate the fractions. Another experiment was performed according to this procedure (flow rate 25.0 mL/h) but without test item ("blank" = column 3).
The water solubility of the test item at a temperature of 20°C was determined (without correction for the purity) to be < 0.042 mg/L.
Reference
Column 1:
Rotation period of the fraction accumulator: 90 min per fraction
Average fraction volume: 16.1 mL
Flow rate: between 10.3 mL/h and 11.0 mL/h
Duration of sampling: about 75 h (50 fractions)
Column 2:
Rotation period of the fraction accumulator: 45 min per fraction
Average fraction volume: 15.6 mL
Flow rate: between 20.0 mL/h and 21.3 mL/h
Duration of sampling: about 72 h (96 fractions)
Column 3 (blank):
Rotation period of the fraction accumulator: 45 min per fraction
Average fraction volume: 15.1 mL
Flow rate: between 19.3 mL/h and 21.3 mL/h
Duration of sampling: about 75 h (100 fractions)
Column-elution method: Column 1
Fraction |
V |
pH |
water solubility |
43 |
16.5 |
5.7 |
<0.042 |
44 |
16.5 |
6.1 |
<0.042 |
45 |
16.5 |
6.4 |
<0.042 |
46 |
16.5 |
6.2 |
<0.042 |
47 |
16.0 |
6.2 |
<0.042 |
According to the guideline the run can be stopped if the concentrations of five fractions do not differ more than ± 30 % without any raising or descending tendency. The content of test item in every fraction is below the detection limit.
Column-elution method: Column 2
Fraction |
V in mL |
pH |
concentration |
86 |
16.0 |
6.9 |
<0.042 |
87 |
16.0 |
6.7 |
<0.042 |
88 |
16.0 |
6.2 |
<0.042 |
89 |
16.0 |
6.5 |
<0.042 |
90 |
16.0 |
6.5 |
<0.042 |
According to the guideline the run can be stopped if the concentrations of five fractions do not differ more than ± 30 % without any raising or descending tendency. The content of test item in every fraction is below the detection limit.
Column-elution method: Column 3 (blank)
Fraction |
V in mL |
pH |
concentration |
90 |
14.5 |
6.4 |
<0.042 |
91 |
14.5 |
6.3 |
<0.042 |
92 |
14.5 |
6.3 |
<0.042 |
93 |
14.5 |
6.3 |
<0.042 |
94 |
14.5 |
6.2 |
<0.042 |
According to the guideline, the data of the fractions 1 to 5 were not taken into account for the following evaluation. The values for the water solubility were calculated from the fractions 43 to 47 for column 1, from the fractions 86 to 90 for column 2, from the fractions 90 to 94 for column 3.
All other fractions were discarded.
Result column 1:
Evaluation of the fractions 43 to 47:
The water solubility was found to be: < 0.042 mg/L (without correction of the purity)
Result column 2:
Evaluation of the fractions 86 to 90:
The water solubility was found to be: < 0.042 mg/L (without correction of the purity)
Result column 3:
Evaluation of the fractions 90 to 94: The blank concentration was found to be < 0.042 mg/L.
The water solubility of the test item at a temperature of 20°C was determined to (without correction for the purity): < 0.042 mg/L
Description of key information
The water solubility of the test item was determined to be < 0.042 mg/L at 20 °C.
Key value for chemical safety assessment
Additional information
The water solubility was determined according to OECD 105 using the column elution method with HPLC analysis.Two identical samples were prepared, one of them was exposed to a flow rate of 12.5 mL/h (column 1), the other one to 25.0 mL/h (column 2). After measurement of the volume, pH and temperature, the fractions were subjected to HPLC analysis. For the determination of the water solubility it was not necessary to combine or to concentrate the fractions. Another experiment was performed according to this procedure (flow rate 25.0 mL/h) but without test item ("blank" = column 3).
The water solubility of the test item at a temperature of 20°C was determined (without correction for the purity) to be < 0.042 mg/L (reference 4.8-1).
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