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EC number: 215-148-3 | CAS number: 1306-24-7
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- yes
- Remarks:
- see "Details on methods" for details.
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Remarks:
- Limit test
- Key result
- Water solubility:
- 5.7 µg/L
- Conc. based on:
- other: Cadmium
- Temp.:
- 20 °C
- pH:
- >= 7.2 - <= 7.5
- Details on results:
- Preliminary test
Precipitation was observed which was independent from sample weight, measurements showed fluctuations.
It was thought that the fluctuations could be caused by (maybe inhomogeneous) impurities. Therefore following confirmation with the sponsor it was decided that it makes more sense to carry out the main test with different loading rates at one temperature (20 ° C).
Main test
The results of the solubility of "Cadmium selenide" in water with different loading rates at 20 °C.
The temperatures of the water baths were between 19.9 and 20.0 °C.
The pH of the solutions was 7.2 to 7.5 at both loading rates.
The solubilities showed constancy (criteria for constancy is a change of concentration of < 15 % compared with the day before) from the first sampling day (after 21 days of stirring) and was stopped after 23 days of stirring.
For calculation of the results all results were taken. The following results were obtained at the different loading rates:
100 mg test item / L: Solubility = < 5.7 µg test item / L
1000 mg test item / L: Solubility = < 5.7 µg test item / L
The replicates per loading rate were comparable. All results are lower than the limit of quantification. - Conclusions:
- The objective of the study was to determine the water solubility of the test substance "Cadmium selenide". For the complete test substance no single analytical method is available. The water solubility was determined using the flask method and estimated by analysis of the element cadmium using Inductively coupled plasma – atomic emission spectroscopy (ICP-AES).
Preliminary tests and measurements showed fluctuations at room temperature. Therefore it was decided with the sponsor to take different loading rates at 20 ° C rather than to determine the water solubility at different temperatures.
Mean water solubility at 20 °C per loading rate:
100 mg test item / L: Solubility = < 5.7 µg test item / L
1000 mg test item / L: Solubility = < 5.7 µg test item / L
In each of the replicates the water solubility of the test substance was less than the limit of quantification (< 5.7 µg/L) of the analytical method. - Executive summary:
The objective of the study was to determine the water solubility of the test substance"Cadmiumselenide". For the complete test substance no single analytical method is available. The water solubility was determined using the flask method and estimated by analysis of the element cadmium using Inductively coupled plasma – atomic emission spectroscopy (ICP-AES).
Preliminary tests and measurements showed fluctuations at room temperature. Therefore it was decided with the sponsor to take different loading rates at 20 ° C rather than to determine the water solubility at different temperatures.
Mean water solubility at 20 °C per loading rate:
100 mg test item / L: Solubility = < 5.7 µg test item / L
1000 mg test item / L: Solubility = < 5.7 µg test item / L
In each of the replicates the water solubility of the test substance was less than the limit of quantification (< 5.7 µg/L) of the analytical method.
Reference
Water solubility with an initial loading rate of 100 mg test item / L
Equilibration time |
Loading rate 100 mg test item / L: Concentration of dissolved µg Cd / L |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Day 21 |
< 3.3 |
< 3.3 |
< 3.3 |
< 3.3 |
Day 22 |
< 3.3 |
< 3.3 |
< 3.3 |
< 3.3 |
Day 23 |
< 3.3 |
< 3.3 |
< 3.3 |
< 3.3 |
Overall mean |
< 3.3 |
|||
Overall standard deviation |
*** |
Equilibration time |
Loading rate 100 mg test item / L: Concentration in µg test item / L |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Day 21 |
< 5.7 |
< 5.7 |
< 5.7 |
< 5.7 |
Day 22 |
< 5.7 |
< 5.7 |
< 5.7 |
< 5.7 |
Day 23 |
< 5.7 |
< 5.7 |
< 5.7 |
< 5.7 |
Overall mean |
< 5.7 |
|||
Overall standard deviation |
*** |
Equilibration time |
Loading rate 100 mg test item / L: pH |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Day 21 |
7.26 |
7.29 |
7.42 |
7.32 |
Day 22 |
7.29 |
7.18 |
7.33 |
7.27 |
Day 23 |
7.38 |
7.22 |
7.41 |
7.34 |
Overall mean |
7.31 |
|||
Overall standard deviation |
0.04 |
Water solubility with an initial loading rate of 1000 mg test item / L
Equilibration time |
Loading rate 1000 mg test item / L: Concentration of dissolved µg Cd / L |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Day 21 |
< 3.3 |
< 3.3 |
< 3.3 |
< 3.3 |
Day 22 |
< 3.3 |
< 3.3 |
< 3.3 |
< 3.3 |
Day 23 |
< 3.3 |
< 3.3 |
< 3.3 |
< 3.3 |
Overall mean |
< 3.3 |
|||
Overall standard deviation |
*** |
Equilibration time |
Loading rate 1000 mg test item / L: Concentration in µg test item / L*) |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Day 21 |
< 5.7 |
< 5.7 |
< 5.7 |
< 5.7 |
Day 22 |
< 5.7 |
< 5.7 |
< 5.7 |
< 5.7 |
Day 23 |
< 5.7 |
< 5.7 |
< 5.7 |
< 5.7 |
Overall mean |
< 5.7 |
|||
Overall standard deviation |
*** |
Equilibration time |
Loading rate 1000 mg test item / L: pH |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Day 21 |
7.38 |
7.24 |
7.40 |
7.34 |
Day 22 |
7.29 |
7.31 |
7.30 |
7.30 |
Day 23 |
7.36 |
7.38 |
7.51 |
7.42 |
Overall mean |
7.35 |
|||
Overall standard deviation |
0.06 |
Analytical method:
A method was validated to determine the content of cadmium in water to calculate the water solubility of the test item “Cadmium selenide”.
Linearity: |
The calibration curve was linear from the quantification limit up to the highest concentration of 100 µg Cd / L. |
Detection limit: |
0.19 µg Cd / L |
Quantification limit: |
0.66 µg Cd / L |
Residual standard deviation: |
24 cps |
Method standard deviation: |
0.24 µg Cd / L |
Relative method standard deviation: |
0.62 % |
Detection limit
0.19 µg Cd / L in the diluted samples, which corresponds to 1.7 µg test item / L calculated with a dilution factor of 5 (rounded up to two significant digits).
Quantification limit
0.66 µg Cd / L in the diluted samples, which corresponds to 5.7 µg test item / L calculated with a dilution factor of 5 (rounded up to two significant digits).
Residual standard deviation
The residual standard deviation was 24 counts per second (cps) in the diluted samples.
Detection limit
0.19 µg Cd / L in the diluted samples, which corresponds to 1.7 µg test item / L calculated with a dilution factor of 5 (rounded up to two significant digits).
Quantification limit
0.66 µg Cd / L in the diluted samples, which corresponds to 5.7 µg test item / L calculated with a dilution factor of 5 (rounded up to two significant digits).
Residual standard deviation
The residual standard deviation was 24 counts per second (cps) in the diluted samples.
Method standard deviation
The method standard deviation was 0.24 µg Cd / L in the diluted samples.
Relative method standard deviation
The relative method standard deviation was 0.62 %.
Accuracy
Sample |
Measured concentration |
Added concentration |
Measured concentration |
Added concentration |
Recovery (%) |
Measurement 1 |
0* |
10 |
10.110 |
10.110 |
101 |
Measurement 2 |
0* |
10 |
10.270 |
10.270 |
103 |
Measurement 3 |
0* |
10 |
10.380 |
10.380 |
104 |
|
|
|
|
Mean: |
103 |
* As the measured concentration of the samples without addition was below the quantification limit, as value of 0 was used for the calculation of the recovery.
The mean recovery of the standard addition experiment was 103 %.
Specificity/ Selectivity
The specificity of the element cadmium was proved by using two different wavelengths which are characteristic and specific for cadmium. The specificity was calculated from the measurements of the spiked samples from the accuracy experiments.
Sample |
Measured concentration |
|
214.400 nm |
228.802 nm |
|
Measurement 1 |
10.110 |
10.400 |
Measurement 2 |
10.270 |
10.290 |
Measurement 3 |
10.380 |
10.420 |
Mean |
10.253 |
10.370 |
The deviation between the two wavelengths was lower than 3 % relative and prove the specificity of the used wavelengths.
Repeatability/ Reproducibility
Sample |
Intensity |
RSD |
|||||
1 |
2 |
3 |
4 |
5 |
6 |
[%] |
|
Level 1 |
634.658 |
638.337 |
640.563 |
644.510 |
643.214 |
638.246 |
0.6 |
Level 2 |
1124.435 |
1136.065 |
1127.236 |
1131.720 |
1124.749 |
1128.226 |
0.4 |
Level 3 |
2645.805 |
2661.940 |
2652.675 |
2663.526 |
2644.614 |
2645.773 |
0.3 |
Level 4 |
5056.573 |
5124.987 |
5116.134 |
5102.950 |
5095.017 |
5113.846 |
0.5 |
Level 5 |
7572.560 |
7608.715 |
7623.466 |
7611.561 |
7587.270 |
7576.395 |
0.3 |
Level 6 |
10120.095 |
10100.092 |
10023.629 |
10123.583 |
10144.631 |
10104.785 |
0.4 |
The relative standard deviations (RSD) lower than 5 % of the different levels prove the precision of the analysis.
The method standard deviation was 0.24 µg Cd / L in the diluted samples.
Relative method standard deviation
The relative method standard deviation was 0.62 %.
Accuracy
Sample |
Measured concentration |
Added concentration |
Measured concentration |
Added concentration |
Recovery (%) |
Measurement 1 |
0* |
10 |
10.110 |
10.110 |
101 |
Measurement 2 |
0* |
10 |
10.270 |
10.270 |
103 |
Measurement 3 |
0* |
10 |
10.380 |
10.380 |
104 |
|
|
|
|
Mean: |
103 |
* As the measured concentration of the samples without addition was below the quantification limit, as value of 0 was used for the calculation of the recovery.
The mean recovery of the standard addition experiment was 103 %.
Specificity/ Selectivity
The specificity of the element cadmium was proved by using two different wavelengths which are characteristic and specific for cadmium. The specificity was calculated from the measurements of the spiked samples from the accuracy experiments.
Sample |
Measured concentration |
|
214.400 nm |
228.802 nm |
|
Measurement 1 |
10.110 |
10.400 |
Measurement 2 |
10.270 |
10.290 |
Measurement 3 |
10.380 |
10.420 |
Mean |
10.253 |
10.370 |
The deviation between the two wavelengths was lower than 3 % relative and prove the specificity of the used wavelengths.
Repeatability/ Reproducibility
Sample |
Intensity |
RSD |
|||||
1 |
2 |
3 |
4 |
5 |
6 |
[%] |
|
Level 1 |
634.658 |
638.337 |
640.563 |
644.510 |
643.214 |
638.246 |
0.6 |
Level 2 |
1124.435 |
1136.065 |
1127.236 |
1131.720 |
1124.749 |
1128.226 |
0.4 |
Level 3 |
2645.805 |
2661.940 |
2652.675 |
2663.526 |
2644.614 |
2645.773 |
0.3 |
Level 4 |
5056.573 |
5124.987 |
5116.134 |
5102.950 |
5095.017 |
5113.846 |
0.5 |
Level 5 |
7572.560 |
7608.715 |
7623.466 |
7611.561 |
7587.270 |
7576.395 |
0.3 |
Level 6 |
10120.095 |
10100.092 |
10023.629 |
10123.583 |
10144.631 |
10104.785 |
0.4 |
The relative standard deviations (RSD) lower than 5 % of the different levels prove the precision of the analysis.
Description of key information
Cadmium selenide was determined to be insoluble in accordance with the flask method (OECD 105).
Key value for chemical safety assessment
- Water solubility:
- 5.7 µg/L
- at the temperature of:
- 20 °C
Additional information
The objective of the study was to determine the water solubility of the test substance"Cadmiumselenide". For the complete test substance no single analytical method is available. The water solubility was determined using the flask method and estimated by analysis of the element cadmium using Inductively coupled plasma – atomic emission spectroscopy (ICP-AES).
Preliminary tests and measurements showed fluctuations at room temperature. Therefore it was decided with the sponsor to take different loading rates at 20 ° C rather than to determine the water solubility at different temperatures.
Mean water solubility at 20 °C per loading rate:
100 mg test item / L: Solubility
= < 5.7 µg test item / L
1000 mg test item / L: Solubility = < 5.7 µg test item / L
In each of the replicates the water solubility of the test substance was less than the limit of quantification (< 5.7 µg/L) of the analytical method.
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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