Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 252-021-1 | CAS number: 34432-92-3
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 26.11.-20.12.2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: This study was carried out in accordance with internationally valid GLP principles.
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION OF TEST SOLUTION
Since the test substance is poorly soluble in test medium at concentrations needed for the test, the saturated solutions of the test substance in test medium were prepared for preliminary and full test. The saturated solutions were prepared by adding measured amounts of the test substance to the test medium. The solutions were stirred for period 72 hours on a shaft stirrer and consequently filtered through 0.45 μm filter. These solutions were used for testing. - Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- - Strain: Brinkmann 1953/SAG 86.81
- Source (laboratory, culture collection): The collection of autotrophic organisms of The Botanic Institute of the Czech Academy of Science, Třeboň
- Age of inoculum (at test initiation): 3 days
- Method of cultivation: The strain culture was preinoculated from the stock solution and cultivated in flasks with the test medium on indirect daylight at laboratory temperature.
ACCLIMATION
- Acclimation period: 3 days
- Culturing media and conditions (same as test or not): same as test - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Test temperature:
- 23.0-23.5°C
- pH:
- 7.8
- Nominal and measured concentrations:
- 100, 56, 31, 17, 9, 5, and 3 mg.L-1 (nominal concentration)
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Erlenmeyers flasks with stoppers venting air
- Aeration: no
- Initial cells density: 5000 cells/1 mL
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 3
GROWTH MEDIUM
- Standard medium used: yes
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: The water with conductivity smaller than 5 μS.cm-1 was used for the preparation of solutions.
- All chemicals used were of analytical grade.
OTHER TEST CONDITIONS
- Lighting: continuous white light, 6900 lux to 6950 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- The density of algae culture was evaluated microscopically at 24, 48 and 72 hours.
- At the beginning and the end of the test the pH of the test mixtures was measured. The light intensity and temperature were measured every 24 hours.
TEST CONCENTRATIONS
- Preliminary test concentrations: 100, 60, 40, 20 and 10 mg.L-1 (nominal concentration)
- On the basis of preliminary test results the test was performed. - Reference substance (positive control):
- yes
- Remarks:
- (potassium dichromate)
- Duration:
- 72 h
- Dose descriptor:
- other: ErC50
- Effect conc.:
- 58.5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95% confidence limit: 53.0 – 64.1 mg•L-1
- Duration:
- 72 h
- Dose descriptor:
- other: EyC50
- Effect conc.:
- 4 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Remarks on result:
- other: 95% confidence limit: 3.0 – 5.0 mg•L-1
- Duration:
- 72 h
- Dose descriptor:
- other: ErC10
- Effect conc.:
- 3.1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: 95% confidence limit: 1.4 – 5.0 mg•L-1
- Duration:
- 72 h
- Dose descriptor:
- other: EyC10
- Effect conc.:
- 0.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Remarks on result:
- other: 95% confidence limit: 0 – 1.2 mg•L-1
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- < 3 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- < 3 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- biomass
- Results with reference substance (positive control):
- - Results with reference substance valid? yes The value EC50 for inhibition of growth rate (72h – ErC50) obtained from last reference test meets the calculated range from the interlaboratory test. The sensitivity of test species and proficiency of our laboratory in test performance was proved.
- Reference test: 72 hour – ErC50 = 0.94 mg.L-1 (95% confidence limit: 0.84 – 1.04 mg.L-1) - Validity criteria fulfilled:
- yes
- Executive summary:
The test substance, Solvent Yellow 124, was tested for growth inhibition on algae Desmodesmus subspicatus.
The test was performed according to method C.3. - Freshwater Algae and Cyanobacteria, Growth Inhibition Test, Commission Regulation (EC) No. 761/2009, Annex IV.
Since the test substance is poorly soluble in test medium at concentrations needed for the test, the saturated solutions of the test substance in test medium were prepared for preliminary and full test. The saturated solutions were prepared by adding measured amounts of the test substance to the test medium. The saturated solutions were prepared by stirring the initital solution for period 72 hours on a shaft stirrer. Finally they were filtered through 0.45 μm filter.
The preliminary test was performed in range of test substance nominal concentrations 10 – 100 mg•L-1. Based on the toxicity of the test substance found in preliminary test, the full test was performed in appropriate concentration range.
Full test was performed in the range of test substance nominal concentrations 3 – 100 mg•L-1.
The nominal concentrations were used for all evaluations and results because study was performed without analytical determination of test substance concentrations. No suitable analytical method was found.
Test results:
72 hour – ErC50 = 58.5 mg•L-1 (nominal concentration)
(95% confidence limit: 53.0 – 64.1 mg•L-1)
72 hour – EyC50 = 4.0 mg•L-1 (nominal concentration)
(95% confidence limit: 3.0 – 5.0 mg•L-1)
72 hour – ErC10 = 3.1 mg•L-1 (nominal concentration)
(95% confidence limit: 1.4 – 5.0 mg•L-1)
72 hour – EyC10 = 0.2 mg•L-1 (nominal concentration)
(95% confidence limit: 0 – 1.2 mg•L-1)
72 hour – NOECr < 3.0 mg•L-1 (nominal concentration)
72 hour – NOECy < 3.0 mg•L-1 (nominal concentration)
Reference
The values of ErC50 and EyC50 were calculated using the software “Toxicita” (Water Research Institute, Ostrava, Czech Republic).
The values and confidence intervals of ErC10 and EyC10 for the test substance were calculated by the software QC.Expert 2.5 © 1998-2000 (product of TriloByte Ltd. Czech Republic).
The determination of NOEC values was done by ANOVA (Analysis of Variance) analysis. Used ANOVA method is the part of statistical software QC.Expert 2.5 © 1998-2000 (TriloByte, Czech Republic).
For the evaluation EC and NOEC values the nominal concentrations were used.
Table: Calculation of EC50 values
|
EC50 mg·L-1 |
Confidence limit |
Approach function |
ErC50(72 h) |
58.5 |
53.0 – 64.1 |
Log-linear |
EyC50(72 h) |
4.0 |
3.0 – 5.0 |
Log-linear |
ErC10(72 h) |
3.1 |
1.4 – 5.0 |
Linear regression |
EyC10(72 h) |
0.2 |
0 - 1.2 |
Linear regression |
Description of key information
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 58.5 mg/L
- EC10 or NOEC for freshwater algae:
- 3 mg/L
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.