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Diss Factsheets
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EC number: - | 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:
- May 09 - June 10, 2016
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- GLP compliance:
- no
- Type of method:
- column elution method
- Key result
- Water solubility:
- > 0.09 - < 10.65 µg/L
- Temp.:
- 20 °C
- pH:
- 6.3
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 07 June-28 July 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 830.7840 (Water Solubility)
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- column elution method
- Water solubility:
- < 6 µg/L
- Temp.:
- 20 °C
- pH:
- 7.6 - 7.7
- Endpoint:
- water solubility
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- May 09 - June 10, 2016
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- GLP compliance:
- no
- Type of method:
- column elution method
- Key result
- Water solubility:
- > 0.09 - < 10.65 µg/L
- Temp.:
- 20 °C
- pH:
- 6.3
- Endpoint:
- water solubility
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 07 June-28 July 2012
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 830.7840 (Water Solubility)
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- column elution method
- Water solubility:
- < 6 µg/L
- Temp.:
- 20 °C
- pH:
- 7.6 - 7.7
Referenceopen allclose all
After substraction of the blank value:
Flow rate [mL/h] |
Fraction No. |
Volume of combined fractions [mL] |
IS [µg/L] |
Solubility of test item [µg/L] |
||
|
|
|
|
Peak 1 |
Peak 2 |
Peak 3 |
12.5 |
1 (1-2) |
20 |
107.91 |
10.27 |
10.65 |
10.13 |
|
2 (3-4) |
20 |
107.91 |
7.52 |
7.04 |
7.06 |
|
3 (5-6) |
20 |
107.91 |
1.63 |
1.88 |
1.68 |
|
4 (7-8) |
20 |
107.91 |
6.66 |
6.89 |
6.91 |
|
5 (9-10) |
20 |
107.91 |
0.87 |
1.32 |
1.15 |
|
6 (11-12) |
20 |
107.91 |
0.69 |
0.60 |
0.68 |
|
7 (13-14) |
20 |
107.91 |
2.56 |
1.97 |
1.59 |
|
8 (15-16) |
20 |
107.91 |
2.18 |
2.06 |
1.96 |
|
|
|
|
|
|
|
6.25 |
1 (1-2) |
20 |
107.91 |
3.31 |
2.87 |
3.07 |
|
2 (3-4) |
20 |
107.91 |
2.50 |
1.98 |
1.90 |
|
3 (5-6) |
20 |
107.91 |
8.23 |
7.85 |
8.07 |
|
4 (7-8) |
20 |
107.91 |
7.98 |
7.51 |
7.88 |
|
5 (9-10) |
20 |
107.91 |
1.56 |
0.98 |
0.85 |
|
6 (11-12) |
20 |
107.91 |
0.36 |
0.24 |
0.09 |
|
7 (13-14) |
20 |
107.91 |
4.89 |
5.38 |
4.68 |
|
8 (15-16) |
20 |
107.91 |
4.25 |
4.12 |
3.86 |
Determination of the water solubility of the test item at flow rates of 12.5 mL/h yielded values in a range 6.92 - 16.50 µg/L (Comp. 1), 7.20 - 17.25 µg/L (Comp. 2) and 7.24 - 16.69µg/L (Comp. 3)
A flow rate of 6.25 mL/h yielded values in a range 6.59 - 14.46 µg/L (Comp. 1), 8.64 - 14.45 µg/L (Comp. 2) and 6.65 - 14.63 µg/L (Comp.3). In contradiction to the OECD Guideline 105 the concentrations differ by more than +-30% and no concentration plateau is reached. For this reason the column elution experiment was repeated to exclude the possibility of an experimental error. The result was confirmed by these experiments, again, no concntration plateau could be achieved. This is, however, due to the low solubility and the three main components of the test item. Therefore, a larger difference has to be regarded acceptable.
The WS was determined at 20 °C. The pH value of the collected aqueous fractions was 6.3.
Stock solutions
Stock solutions of the test substance were prepared in acetonitrile at concentrations of 2470 ‑ 3950 mg/L.
Calibration solutions
Calibration solutions in the concentration range of 3 – 700 µg/L were prepared from two stock solutions. The end solution of the calibration solutions was 50/50 (v/v) acetonitrile/water.
Calibration solutions were injected in duplicate. Test samples were analysed by single injection.
Calibration curves were constructed using six concentrations. For each concentration, two responses were used. Linear regression analysis was performed using the least squares method with a 1/concentration2weighting factor. The coefficient of correlation (r) was > 0.99 for each curve.
Main study - water solubility of the test substance
Flow rate |
Sample no. |
Concentration analysed |
pH |
||||
Individual |
Mean1 |
CV |
Mean2 |
MD3 |
|
||
|
|
|
|
|
|
|
|
24 |
1 |
6.11 |
6.07 |
12 |
|
|
7.8 |
|
2 |
5.97 |
|
|
|
|
|
|
3 |
5.694 |
|
|
|
|
|
|
4 |
4.624 |
|
|
|
|
|
|
5 |
11.65 |
|
|
|
|
|
|
6 |
7.14 |
|
|
|
|
|
|
7 |
7.02 |
|
|
|
|
|
|
8 |
5.66 |
|
|
|
|
|
|
9 |
6.33 |
|
|
|
|
|
|
10 |
6.04 |
|
|
|
|
|
|
|
|
|
|
|
|
|
12 |
1 |
<6.00 |
<6.00 |
n.a. |
|
|
7.7 |
|
2 |
<6.00 |
|
|
|
|
|
|
3 |
<6.00 |
|
|
|
|
|
|
4 |
<6.00 |
|
|
|
|
|
|
5 |
<6.00 |
|
|
|
|
|
|
6 |
<6.00 |
|
|
|
|
|
|
7 |
<6.00 |
|
|
|
|
|
|
8 |
<6.00 |
|
|
|
|
|
|
9 |
12.45 |
|
|
|
|
|
|
10 |
<6.00 |
|
|
|
|
|
|
|
|
|
|
|
|
|
6 |
1 |
<6.00 |
<6.00 |
n.a. |
<6.00 |
n.a. |
7.6 |
|
2 |
<6.00 |
|
|
|
|
|
|
3 |
<6.00 |
|
|
|
|
|
|
4 |
<6.00 |
|
|
|
|
|
|
5 |
<6.00 |
|
|
|
|
|
|
6 |
<6.00 |
|
|
|
|
|
|
7 |
<6.00 |
|
|
|
|
|
|
8 |
<6.00 |
|
|
|
|
|
|
9 |
<6.00 |
|
|
|
|
|
|
10 |
<6.00 |
|
|
|
|
|
After substraction of the blank value:
Flow rate [mL/h] |
Fraction No. |
Volume of combined fractions [mL] |
IS [µg/L] |
Solubility of test item [µg/L] |
||
|
|
|
|
Peak 1 |
Peak 2 |
Peak 3 |
12.5 |
1 (1-2) |
20 |
107.91 |
10.27 |
10.65 |
10.13 |
|
2 (3-4) |
20 |
107.91 |
7.52 |
7.04 |
7.06 |
|
3 (5-6) |
20 |
107.91 |
1.63 |
1.88 |
1.68 |
|
4 (7-8) |
20 |
107.91 |
6.66 |
6.89 |
6.91 |
|
5 (9-10) |
20 |
107.91 |
0.87 |
1.32 |
1.15 |
|
6 (11-12) |
20 |
107.91 |
0.69 |
0.60 |
0.68 |
|
7 (13-14) |
20 |
107.91 |
2.56 |
1.97 |
1.59 |
|
8 (15-16) |
20 |
107.91 |
2.18 |
2.06 |
1.96 |
|
|
|
|
|
|
|
6.25 |
1 (1-2) |
20 |
107.91 |
3.31 |
2.87 |
3.07 |
|
2 (3-4) |
20 |
107.91 |
2.50 |
1.98 |
1.90 |
|
3 (5-6) |
20 |
107.91 |
8.23 |
7.85 |
8.07 |
|
4 (7-8) |
20 |
107.91 |
7.98 |
7.51 |
7.88 |
|
5 (9-10) |
20 |
107.91 |
1.56 |
0.98 |
0.85 |
|
6 (11-12) |
20 |
107.91 |
0.36 |
0.24 |
0.09 |
|
7 (13-14) |
20 |
107.91 |
4.89 |
5.38 |
4.68 |
|
8 (15-16) |
20 |
107.91 |
4.25 |
4.12 |
3.86 |
Determination of the water solubility of the test item at flow rates of 12.5 mL/h yielded values in a range 6.92 - 16.50 µg/L (Comp. 1), 7.20 - 17.25 µg/L (Comp. 2) and 7.24 - 16.69µg/L (Comp. 3)
A flow rate of 6.25 mL/h yielded values in a range 6.59 - 14.46 µg/L (Comp. 1), 8.64 - 14.45 µg/L (Comp. 2) and 6.65 - 14.63 µg/L (Comp.3). In contradiction to the OECD Guideline 105 the concentrations differ by more than +-30% and no concentration plateau is reached. For this reason the column elution experiment was repeated to exclude the possibility of an experimental error. The result was confirmed by these experiments, again, no concntration plateau could be achieved. This is, however, due to the low solubility and the three main components of the test item. Therefore, a larger difference has to be regarded acceptable.
The WS was determined at 20 °C. The pH value of the collected aqueous fractions was 6.3.
Stock solutions
Stock solutions of the test substance were prepared in acetonitrile at concentrations of 2470 ‑ 3950 mg/L.
Calibration solutions
Calibration solutions in the concentration range of 3 – 700 µg/L were prepared from two stock solutions. The end solution of the calibration solutions was 50/50 (v/v) acetonitrile/water.
Calibration solutions were injected in duplicate. Test samples were analysed by single injection.
Calibration curves were constructed using six concentrations. For each concentration, two responses were used. Linear regression analysis was performed using the least squares method with a 1/concentration2weighting factor. The coefficient of correlation (r) was > 0.99 for each curve.
Main study - water solubility of the test substance
Flow rate |
Sample no. |
Concentration analysed |
pH |
||||
Individual |
Mean1 |
CV |
Mean2 |
MD3 |
|
||
|
|
|
|
|
|
|
|
24 |
1 |
6.11 |
6.07 |
12 |
|
|
7.8 |
|
2 |
5.97 |
|
|
|
|
|
|
3 |
5.694 |
|
|
|
|
|
|
4 |
4.624 |
|
|
|
|
|
|
5 |
11.65 |
|
|
|
|
|
|
6 |
7.14 |
|
|
|
|
|
|
7 |
7.02 |
|
|
|
|
|
|
8 |
5.66 |
|
|
|
|
|
|
9 |
6.33 |
|
|
|
|
|
|
10 |
6.04 |
|
|
|
|
|
|
|
|
|
|
|
|
|
12 |
1 |
<6.00 |
<6.00 |
n.a. |
|
|
7.7 |
|
2 |
<6.00 |
|
|
|
|
|
|
3 |
<6.00 |
|
|
|
|
|
|
4 |
<6.00 |
|
|
|
|
|
|
5 |
<6.00 |
|
|
|
|
|
|
6 |
<6.00 |
|
|
|
|
|
|
7 |
<6.00 |
|
|
|
|
|
|
8 |
<6.00 |
|
|
|
|
|
|
9 |
12.45 |
|
|
|
|
|
|
10 |
<6.00 |
|
|
|
|
|
|
|
|
|
|
|
|
|
6 |
1 |
<6.00 |
<6.00 |
n.a. |
<6.00 |
n.a. |
7.6 |
|
2 |
<6.00 |
|
|
|
|
|
|
3 |
<6.00 |
|
|
|
|
|
|
4 |
<6.00 |
|
|
|
|
|
|
5 |
<6.00 |
|
|
|
|
|
|
6 |
<6.00 |
|
|
|
|
|
|
7 |
<6.00 |
|
|
|
|
|
|
8 |
<6.00 |
|
|
|
|
|
|
9 |
<6.00 |
|
|
|
|
|
|
10 |
<6.00 |
|
|
|
|
|
Description of key information
Key value for chemical safety assessment
- Water solubility:
- 0.01 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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.