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EC number: 617-606-1 | CAS number: 84656-75-7
- 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:
- 24.04.-08.05.2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- no
- GLP compliance:
- no
- Type of method:
- column elution method
- Key result
- Water solubility:
- < 0.047 mg/L
- Temp.:
- 20 °C
- Remarks on result:
- other: pH not relevant
- Conclusions:
- The water solubility of the test item at a temperature of 20°C was found to be below the quantification limit: < 47 µg/L.
- Executive summary:
The water solubility of the test item was determined according to OECD 105 and Regulation (EC) No. 440/2008 method A.6 using the column elution method with HPLC analysis. 104.9 mg of the test item were dissolved in 100 ml acetone using ultrasonic bath for 10 min 25 ml of this solution was added to about 3 g of sea sand and the mixture was shaken. This procedure was performed for column 1 and column 2. The solvent was then removed under reduced pressure using a rotary evaporator (50 °C, 40 mbar). The dry residues were placed into the columns of the test apparatus, which were afterwards filled with water (test temperature: 20 °C; pH of water at 22.9 °C; 5.6). After a swelling time of 2 h the pump was started to rinse the substance coated sand with distilled water. Two identical columns were prepared, one of them was exposed to a flow rate of about 12.5 ml/h (column 1), the other one to about 25.0 ml/h (column 2). Another experiment was performed according to this procedure but without test item ("blank" = column 3). The concentration of test item was determined by means of HPLC. Therefore, the aqueous fractions were diluted from 0.5 ml to 1 ml with acetonitrile. The volumes of all fractions were measured. For the analysed fractions the pH values and the temperatures were measured, too. At the end of the study it was confirmed that residual test item remained on the columns. The residual test item was eluted with 50 ml acetone. The eluate was diluted from 0.1 ml to 20 ml with acetonitrile and again from 0.1 ml to 1 ml with acetonitrile and distilled water (50:50 % v/v). Subsequently the concentration was quantified by HPLC.
The concentration of the test item was quantified by HPLC. The pH of each sample was recorded. The water solubility of the test item at a temperature of 20°C was found to be below the quantification limit: < 47 µg/L.
Reference
Table 1: Recovery
All recovery values are calculated from the measured and unrounded concentration values and not from the rounded values given in Table 1. The recovery of the standards indicated a sufficient accuracy of the analytical method.
Standard | Measured concentration /µg/L | % Recovery (mean values) |
E (c = 397.5 µg/L) | 406.33/408.27 | 102.5 |
G (c= 132.5 µg/L) | 124.62/133.29 137.76/134.89 |
97.3 102.9 |
H (c= 23.40 µg/L) | 23.39/24.78 | 102.9 |
I (c = 46.80 µg/L) | 43.43/42.78 | 92.1 |
J (c = 260 µg/L) | 242.85/237.01 | 92.3 |
Table 2: Repeatability
The repeatability was checked by measuring standard F six-fold. The resulting area was used to calculate the standard deviation and the variation coefficient.
Measurement No. | Area / mAU*s |
1 | 59.400 |
2 | 59.887 |
3 | 59.580 |
4 | 59.800 |
5 | 59.594 |
6 | 59.679 |
Mean value | 59.7 |
Standard deviation | 0.2 |
Variation coefficient / % | 0.3 |
The accuracy of the analytical method was evaluated as sufficient as the variation coefficient of the repeatability measurements was < 2.
Different amounts of the test item and water were stirred at room temperature until the mixture appeared dissolved or the water solubility could be estimated to be below 10 mg/I.
Table 3: Results of the preliminary test
Amount of test item / mg |
Total volume of demineralized water / mL |
Appearance of mixture |
10.7 | 100 | not dissolved |
11.3 | 500 | not dissolved |
3.5 | 500 | not dissolved |
The solubility of the test item in water was found to be below 7.0 mg/I (without correction of the purity). Therefore the column elution method was performed for the determination of the water solubility of the test item.
Table 4: Column elution method, column 1 (approximately 12.0 mL/h)
Fraction No. | V/mL | pH | water solubility /µg/L |
21 | 18.0 | 5.7 | <47 |
22 | 17.5 | 5.7 | <47 |
23 | 17.5 | 5.7 | <47 |
24 | 17.5 | 5.7 | <47 |
25 | 17.5 | 5.7 | <47 |
The water solubility was found to be below the quantification limit of 47 µg/L.
Table 5: Column elution method, column 2 (approximately 25 mL/h)
Fraction No. |
V/mL |
pH |
water solubility /µg/L |
48 |
18.0 |
5.6 |
<47 |
49 |
18.0 |
5.6 |
<47 |
50 |
18.0 |
5.7 |
<47 |
51 |
18.0 |
5.7 |
<47 |
52 |
18.0 |
5.6 |
<47 |
The water solubility was found to be below the quantification limit of 47 µg/L.
In both columns the concentration of five consecutive fractions was constant within ± 30 %. No increasing or decreasing tendency was observed.
Table 6: Column elution method, column 3 (blank)
Fraction No. |
V/mL |
pH |
water solubility /µg/L |
49 |
17.5 |
5.6 |
<47 |
50 |
17.5 |
5.6 |
<47 |
51 |
17.5 |
5.6 |
<47 |
52 |
17.5 |
5.6 |
<47 |
53 |
17.5 |
5.6 |
<47 |
The blank concentration was found to be below the quantification limit of 47 µg/L.
Table 7: Coating check
|
Amount of test item used for coating /mg |
Measured concentration of test item in eluate /mg/L |
Amount of test item eluted / mg
|
Column 1 |
26.2 |
0.246/0.245 |
24.6 |
Column 2 |
0.232/0.231 |
23.2 |
The coating check was successful. There was enough residual test item remained an the columns after the performance of the column elution method.
Description of key information
The water solubility of the test item at a temperature of 20°C was found to be below the quantification limit: < 47 µg/L.
Key value for chemical safety assessment
Additional information
The water solubility of the test item was determined according to OECD 105 and Regulation (EC) No. 440/2008 method A.6 using the column elution method with HPLC analysis. 104.9 mg of the test item were dissolved in 100 ml acetone using ultrasonic bath for 10 min 25 ml of this solution was added to about 3 g of sea sand and the mixture was shaken. This procedure was performed for column 1 and column 2. The solvent was then removed under reduced pressure using a rotary evaporator (50 °C, 40 mbar). The dry residues were placed into the columns of the test apparatus, which were afterwards filled with water (test temperature: 20 °C; pH of water at 22.9 °C; 5.6). After a swelling time of 2 h the pump was started to rinse the substance coated sand with distilled water. Two identical columns were prepared, one of them was exposed to a flow rate of about 12.5 ml/h (column 1), the other one to about 25.0 ml/h (column 2). Another experiment was performed according to this procedure but without test item ("blank" = column 3). The concentration of test item was determined by means of HPLC. Therefore, the aqueous fractions were diluted from 0.5 ml to 1 ml with acetonitrile. The volumes of all fractions were measured. For the analysed fractions the pH values and the temperatures were measured, too. At the end of the study it was confirmed that residual test item remained on the columns. The residual test item was eluted with 50 ml acetone. The eluate was diluted from 0.1 ml to 20 ml with acetonitrile and again from 0.1 ml to 1 ml with acetonitrile and distilled water (50:50 % v/v). Subsequently the concentration was quantified by HPLC.
The concentration of the test item was quantified by HPLC. The pH of each sample was recorded. The water solubility of the test item at a temperature of 20°C was found to be below the quantification limit: < 47 µg/L.
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