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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
Additional information on environmental fate and behaviour
Administrative data
- Endpoint:
- additional information on environmental fate and behaviour
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 29 October 2018 to 04 December 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2019
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other:
- Version / remarks:
- OECD 29: Transformation/Dissolution of Metals and Metal Compounds in Aqueous Media, adopted
on 23 July 2001. - Deviations:
- not specified
- GLP compliance:
- yes
Test material
- Reference substance name:
- Cadmium selenide
- EC Number:
- 215-148-3
- EC Name:
- Cadmium selenide
- Cas Number:
- 1306-24-7
- Molecular formula:
- CdSe
- IUPAC Name:
- cadmium selenide
- Test material form:
- solid
Constituent 1
Results and discussion
Any other information on results incl. tables
Screening test
The results showed the lowest solubility of test item in the buffering solution with pH 8.5. As there were no observable deviation between the solutions with pH 6 and pH 7 it was decided to use the buff
ering solution with pH 6 for the full transformation/ dissolution test. The diluted cadmium contents of the test vessels with pH 6 varied between 88 μg / L and 110 μg / L.
All oxygen levels were within the recommended range of the OECD Test Guideline 29.
Main test
The results of the transformation/ dissolution of "Cadmium selenide" in dissolution medium with a pH of approximately 6 with different loading rates at 22 ± 2°C are listed in sections 6.2.2 and 6.2.3.
The temperatures during the whole experiment were between 20.8 and 23.5 °C.
The pH values of the solutions were between 6.1 and 6.3 at all loading rates and therefore remained constant during the whole experiment.
The following results were obtained at the different loading rates:
1 mg test item / L: 23 μg Cd / L after 7 days (short term test)
Solubility equilibrium of 43.7 ± 4.6 μg Cd / L has been reached between 336 h (14 days) and 672 h (28 days) because three subsequent total dissolved metal concentration data points vary no more
than 15 % according to the OECD Test Guideline 29. 10 mg test item / L: 171 μg Cd / L after 7 days (short term test)
No solubility equilibrium have been reached during the test period of seven days.
100 mg test item / L: 551 μg Cd / L after 7 days (short term test)
No solubility equilibrium have been reached during the test period of seven days.
All oxygen levels were within the recommended range of the OECD Test Guideline 29.
The numerical data in the tables have been rounded for presentation, a manual recalculation therefore may yield slightly different results to those given in the tables.
Screening test
Buffering solution with pH 6
Equilibration time |
Concentration of dissolved µg Cd / L |
pH |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
||
Vessel 1 |
110 |
106 |
109 |
108 |
6.0 |
Vessel 2 |
105 |
101 |
103 |
103 |
6.0 |
Vessel 3 |
91 |
88 |
91 |
90 |
5.9 |
Overall mean |
100 |
6.0 |
|||
Overall standard deviation |
8 |
0.0 |
Buffering solution with pH 7
Equilibration time |
Concentration of dissolved µg Cd / L |
pH |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
||
Vessel 1 |
81 |
81 |
81 |
81 |
7.0 |
Vessel 2 |
111 |
111 |
112 |
111 |
7.0 |
Vessel 3 |
105 |
105 |
105 |
105 |
7.1 |
Overall mean |
99 |
7.0 |
|||
Overall standard deviation |
14 |
0.1 |
Buffering solution with pH 8.5
Equilibration time |
Concentration of dissolved µg Cd / L |
pH |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
||
Vessel 1 |
56 |
56 |
58 |
57 |
8.4 |
Vessel 2 |
53 |
53 |
54 |
53 |
8.4 |
Vessel 3 |
74 |
74 |
74 |
74 |
8.5 |
Overall mean |
61 |
8.4 |
|||
Overall standard deviation |
10 |
0.1 |
Short term dissolution tests
Transformation / dissolution - initial loading rate of 10 mg test item / L
Equilibration time |
Concentration of dissolved µg Cd / L |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Start = 0 h |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
2 h |
3.9 |
5.5 |
3.7 |
4.4 |
6 h |
11 |
19 |
12 |
14 |
24 h (=1 d) |
18 |
33 |
21 |
24 |
72 h (=3 d) |
72 |
140 |
92 |
102 |
168 h (=7 d) |
140 |
185 |
188 |
171 |
Equilibration time |
Concentration in µg test item / L |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Start = 0 h |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
2 h |
6.6 |
9.4 |
6.3 |
7.4 |
6 h |
19 |
32 |
21 |
24 |
24 h (=1 d) |
31 |
56 |
36 |
41 |
72 h (=3 d) |
123 |
239 |
157 |
173 |
168 h (=7 d) |
238 |
315 |
320 |
291 |
Equilibration time |
pH |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Start = 0 h |
6.3 |
6.3 |
6.3 |
6.3 |
2 h |
6.1 |
6.2 |
6.2 |
6.2 |
6 h |
6.2 |
6.2 |
6.2 |
6.2 |
24 h (=1 d) |
6.2 |
6.2 |
6.1 |
6.2 |
72 h (=3 d) |
6.3 |
6.3 |
6.3 |
6.3 |
168 h (=7 d) |
6.3 |
6.3 |
6.2 |
6.2 |
Transformation / dissolution - initial loading rate of 100 mg test item / L
Equilibration time |
Concentration of dissolved µg Cd / L |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Start = 0 h |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
2 h |
29 |
30 |
23 |
28 |
6 h |
80 |
90 |
72 |
80 |
24 h (=1 d) |
117 |
136 |
111 |
121 |
72 h (=3 d) |
323 |
406 |
332 |
354 |
168 h (=7 d) |
529 |
587 |
537 |
551 |
Equilibration time |
Concentration in µg test item / L |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Start = 0 h |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
2 h |
50 |
52 |
40 |
47 |
6 h |
137 |
152 |
122 |
137 |
24 h (=1 d) |
199 |
232 |
189 |
207 |
72 h (=3 d) |
550 |
691 |
565 |
602 |
168 h (=7 d) |
900 |
999 |
913 |
937 |
Equilibration time |
pH |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Start = 0 h |
6.3 |
6.3 |
6.3 |
6.3 |
2 h |
6.1 |
6.1 |
6.1 |
6.1 |
6 h |
6.1 |
6.2 |
6.1 |
6.1 |
24 h (=1 d) |
6.2 |
6.2 |
6.1 |
6.2 |
72 h (=3 d) |
6.3 |
6.2 |
6.2 |
6.2 |
168 h (=7 d) |
6.2 |
6.3 |
6.2 |
6.3 |
Long term dissolution test
Transformation / dissolution - initial loading rate of 1 mg test item / L
Equilibration time |
Concentration of dissolved µg Cd / L |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Start = 0 h |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
2 h |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
6 h |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
24 h (=1 d) |
3.5 |
3.8 |
3.1 |
3.5 |
72 h (=3 d) |
14 |
14 |
11 |
13 |
168 h (=7 d) |
26 |
24 |
19 |
23 |
336 h (=14 d) |
41 |
42 |
33 |
39 |
504 h (=21 d) |
44 |
46 |
44 |
44 |
672 h (=28 d) |
44 |
52 |
48 |
48 |
Equilibration time |
Concentration in µg test item / L |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Start = 0 h |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
2 h |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
6 h |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
24 h (=1 d) |
5.9 |
6.5 |
5.3 |
5.9 |
72 h (=3 d) |
24 |
23 |
18 |
22 |
168 h (=7 d) |
44 |
41 |
33 |
39 |
336 h (=14 d) |
71 |
71 |
57 |
66 |
504 h (=21 d) |
75 |
78 |
75 |
76 |
672 h (=28 d) |
75 |
88 |
82 |
82 |
Equilibration time |
pH |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Start = 0 h |
6.2 |
6.3 |
6.3 |
6.3 |
2 h |
6.1 |
6.2 |
6.1 |
6.1 |
6 h |
6.2 |
6.2 |
6.2 |
6.2 |
24 h (=1 d) |
6.2 |
6.1 |
6.1 |
6.1 |
72 h (=3 d) |
6.2 |
6.3 |
6.3 |
6.2 |
168 h (=7 d) |
6.1 |
6.2 |
6.2 |
6.2 |
336 h (=14 d) |
6.2 |
6.2 |
6.2 |
6.2 |
504 h (=21 d) |
6.3 |
6.3 |
6.2 |
6.3 |
672 h (=28 d) |
6.3 |
6.2 |
6.3 |
6.3 |
Blank solutions for short and long term dissolution test
Equilibration time |
Concentration of dissolved µg Cd / L |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Start = 0 h |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
2 h |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
6 h |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
24 h (=1 d) |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
72 h (=3 d) |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
168 h (=7 d) |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
336 h (=14 d) |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
504 h (=21 d) |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
672 h (=28 d) |
< 3.1 |
< 3.1 |
< 3.1 |
< 3.1 |
Equilibration time |
Concentration in µg test item / L |
|||
1streplicate |
2ndreplicate |
3rdreplicate |
Mean |
|
Start = 0 h |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
2 h |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
6 h |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
24 h (=1 d) |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
72 h (=3 d) |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
168 h (=7 d) |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
336 h (=14 d) |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
504 h (=21 d) |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
672 h (=28 d) |
< 5.2 |
< 5.2 |
< 5.2 |
< 5.2 |
Equilibration time |
pH |
Start = 0 h |
6.3 |
2 h |
6.2 |
6 h |
6.2 |
24 h (=1 d) |
6.2 |
72 h (=3 d) |
6.2 |
168 h (=7 d) |
6.2 |
336 h (=14 d) |
6.2 |
504 h (=21 d) |
6.2 |
672 h (=28 d) |
6.3 |
Validation Results
Linearity
The calibration curve was linear from the quantification limit up to the highest concentration of 100 µg Cd / L. The coefficient of determination (R2) was 0.99996.
The following functions were received:
y [cps] = 94.01893 [cps/(µg / L)] * x [µg / L] + 79.45502 [cps]
where
x = nominal concentration of cadmium in µg / L
y = signal in counts per second (cps)
with the following ranges respectively confidence intervals for slope and intercept of the linear function:
Slope: 93.83990 – 94.19796 = 94.01893±0.17903
Intercept: 70.15852 – 88.75152 = 79.45502±9.29650
Detection limit
0.17 µg Cd / L in the diluted samples, which corresponds to 1.4 µg test item / L calculated with a dilution factor of 5 (rounded to two significant digits).
Quantification limit
0.61 µg Cd / L in the diluted samples, which corresponds to 5.2 µg test item / L calculated with a dilution factor of 5 (rounded to two significant digits).
Residual standard deviation
The residual standard deviation was 20 counts per second (cps) in the diluted samples.
Method standard deviation
The method standard deviation was 0.22 µg Cd / L in the diluted samples.
Relative method standard deviation
The relative method standard deviation was 0.57 %.
Accuracy
Sample |
Measured concentration |
Added concentration |
Measured concentration |
Added concentration |
Recovery (%) |
Measurement 1 |
14.21 |
15 |
29.45 |
15.24 |
102 |
Measurement 2 |
14.45 |
15 |
29.47 |
15.02 |
100 |
Measurement 3 |
14.63 |
15 |
29.54 |
14.91 |
99 |
|
|
|
|
Mean |
100 |
The mean recovery of the standard addition experiment was 100 %.
Reproducibility
|
Concentration of dissolved µg Cd / L |
|||||
1streplicate |
2ndreplicate |
3rdreplicate |
Within- vessel |
|||
Mean |
Standard deviation |
Relative Standard deviation |
||||
Vessel 1 |
110 |
106 |
109 |
108 |
2 |
2 |
Vessel 2 |
105 |
101 |
103 |
103 |
2 |
2 |
Vessel 3 |
91 |
88 |
91 |
90 |
2 |
2 |
Vessel 4 |
117 |
117 |
117 |
117 |
0 |
0 |
Vessel 5 |
137 |
135 |
137 |
136 |
1 |
1 |
Vessel 6 |
111 |
111 |
110 |
111 |
1 |
0 |
Mean between-vessel |
111 |
--- |
--- |
|||
Standard deviation between-vessel |
15 |
--- |
--- |
|||
Relative standard deviation between-vessel [%] |
14 |
--- |
--- |
The calculated relative standard deviations (RSD) of the results were lower than the recommended values (< 20 % between-vessel and < 10% within- vessel) and therefore prove the reproducibility of the analysis.
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 |
15.24 |
15.22 |
Measurement 2 |
15.02 |
14.92 |
Measurement 3 |
14.91 |
15.11 |
Mean |
15.06 |
15.08 |
The deviation between the two wavelengths was lower than 1 % relative and prove the specificity of the used wavelengths.
Applicant's summary and conclusion
- Conclusions:
- At a loading of 1 mg test item / L, the dissolved mean concentration was 23 μg Cd / L (39 μg test it em / L) after the 7 days transformation / dissolution test and the equilibrium concentration observed within the test period of 28 days was 43.7 μg Cd / L (74 μg test item / L).
At a loading of 10 mg test item / L, the dissolved mean concentration was 171 μg Cd / L (291 μg test item / L) after the 7 days transformation / dissolution test. Within the test period of 7 days no equilibrium was observed.
At a loading of 100 mg test item / L, the dissolved mean concentration was 551 μg Cd / L (937 μg test item / L) after the 7 days transformation / dissolution test. Within the test period of 7 days no equilibrium was observed. - Executive summary:
The objective of the study was to determine the transformation / dissolution of the test substance"Cadmiumselenide". For the complete test substance no single analytical method is available. The transformation / dissolution was therefore estimated by analysis of the element cadmium.
The screening test showed that at pH of 6 maximises the dissolution of cadmium selenide. Therefore the full transformation/ dissolution tests were performed with a dissolution media with this pH value.
Main experiments
Short term transformation / dissolution at 22±2 °C per loading rate:
1 mg test item / L: 23 µg Cd / L after 7 days
pH range: 6.1 to 6.310 mg test item / L: 171 µg Cd / L after 7 days
pH range: 6.1 to 6.3100 mg test item / L: 551 µg Cd / L after 7 days
pH range: 6.1 to 6.3Long term transformation / dissolution at 22±2 °C per loading rate:
1 mg test item / L: Solubility equilibrium of 43.7 ± 4.6 µg Cd / L has been reached between 336 h (14 days) and 672 h (28 days)
pH range: 6.1 to 6.3In each of the blank vessels without test item the content of diluted test item was less than the limit of quantification (< 5.2 µg / L) of the analytical method.
The observed levels and variations in temperature, pH and oxygen concentrations were in compliance with the test guideline OECD 29.
The transformation curves can be found in Appendix 3 as plots of time and measured cadmium concentrations.
Conclusion
At a loading of 1 mg test item / L, the dissolved mean concentration was 23 µg Cd / L (39 µg test item / L) after the 7 days transformation / dissolution test and the equilibrium concentration observed within the test period of 28 days was 43.7 µg Cd / L (74 µg test item / L).
At a loading of 10 mg test item / L, the dissolved mean concentration was 171 µg Cd / L (291 µg test item / L) after the 7 days transformation / dissolution test. Within the test period of 7 days no equilibrium was observed.
At a loading of 100 mg test item / L, the dissolved mean concentration was 551 µg Cd / L (937 µg test item / L) after the 7 days transformation / dissolution test. Within the test period of 7 days no equilibrium was observed.
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