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EC number: 220-562-2 | CAS number: 2814-77-9
- 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:
- 02.08. to 15.08.2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.3 (Algal Inhibition test)
- Version / remarks:
- Freshwater Algae and Cyanobacteria, Growth Inhibition Test, Commission Regulation (EC) No. No.2016/266
- Deviations:
- yes
- Remarks:
- without impact (see Any other information on ... methods )
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
The stock solutions of the test item were prepared in the test medium. 100 mg of the test item was weighed into 1000 mL of the test medium for the preliminary and limit test. The stock solutions were ultrasonicated for 30 minutes and stirred for period 1 hours. The concentrations of test solutions used in the preliminary test were obtained by dilution of the stock solution with test medium.
Preliminary test: The volume of the test solution was 50 mL in each testing flask. The initial density of 5 000 cells per mL was used in the test. The flasks were placed on a shaker under the lighting ramp and were incubated under continuous illumination and shaking for 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. The density of algae culture was evaluated microscopically at 24, 48 and 72 hours. The cell density was measured by direct counting of living cells in Burker´s counting chamber. The growth rates (u) and the yield (Y) and subsequently percentage reduction of growth rate and percentage inhibition of yield were calculated from obtained values.
- Differential loading:
The preliminary test was performed in a range of the test item nominal concentrations 1 – 100 mg·L-1. Based on low toxicity of the test item found in the preliminary test, the limit test with the test item nominal concentration 100 mg·L-1 was performed subsequently.
- Controls: The test contained six parallel series of the test item concentration and six controls without the test item.
- Chemical name of vehicle (organic solvent, emulsifier or dispersant):
Test medium - the water with conductivity smaller than 5 μS·cm-1 was used for the preparation of solutions. All chemicals used were of analytical-grade.
- Concentration of vehicle in test medium (stock solution and final test solution(s) or suspension(s) including control(s)):
The volume of the test solution was 50 mL in each testing flask. - Test organisms (species):
- Desmodesmus subspicatus (previous name: Scenedesmus subspicatus)
- Details on test organisms:
- TEST ORGANISM
- Common name: The green freshwater algae Desmodesmus subspicatus
- Strain: Desmodesmus subspicatus Brinkmann 1953/SAG 86.81
- Source: from the collection of autotrophic organisms of The Botanic Institute of the Czech Academy of Science, Třeboň
- Age of inoculum (at test initiation): The strain culture was always set to pre-culturing of cells for 3-4 days before the start of the test. Inoculum culture was kept 3-4 days under conditions at which the test was performed.
- 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. Algae inoculum for the test was sampled from exponentially growing inoculum culture.
ACCLIMATION
- Acclimation period: 3-4 days
- Culturing media and conditions (same as test or not): same as test - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 72 h
- Test temperature:
- 22.0 – 22.5 °C
- pH:
- 8.1
- Conductivity:
- 1.66 µS·cm-1
- Nominal and measured concentrations:
- 100 mg·L-1
The study will be performed without analytical determination of the test item concentrations. - Details on test conditions:
- Preliminary test
Range of nominal concentration: 1-100 mg/l
Stock solution of the test substance: 100.06 mg / 1000 mL-1
Test concentrations: 100, 50, 10, 5 and 1 mg/l
Conductivity of deionized water: 1.58 μS/cm
pH of the test medium: 8.1
Volume of inoculated algae culture: 1.07 mL in 200 mL of mixture
Lighting during the test: 7442 – 7450 lux
Temperature during the test: 22.0°C
Inicial density: 5000 cells per mL
Limit test
Stock solution of the test substance: 100.05 mg·L-1 / 1000 mL-1
The test concentration: 100 mg·L-1 nominal
Conductivity of deionized water: 1.66 µS·cm-1
pH of the test medium: 8.1
Volume of inoculum algae culture: 4.0 mL in 500 mL mixture
Lighting during the test: 7438 – 7450 lux
Temperature during the test: 22.0 – 22.5 °C
Inicial density: 5000 cells per 1ml
Testing mixtures were incubated in the Erlenmeyers’ flasks. The test contained six parallel series of the test item concentration and six controls without the test item.
The volume of the test solution was 50 mL in each testing flask. The flasks were placed on a shaker under the lighting ramp and were incubated under continuous illumination and shaking for 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. The density of algae culture was evaluated microscopically at 24, 48 and 72 hours. The cell density was measured by direct counting of living cells in Burker´s counting chamber. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Duration:
- 72 h
- Dose descriptor:
- NOEC
- Effect conc.:
- < 1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Results with reference substance (positive control):
- - Results with reference substance valid? Yes
The value EC50 for inhibition of growth rate (72h – ErC50) obtained from our 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 = 1.02 mg·L-1 (95% confidence limit: 0.84 – 1.23 mg·L-1)
Interlaboratory test: 72 hour – ErC50 = 0.51 – 1.19 mg·L-1 - Validity criteria fulfilled:
- yes
- Conclusions:
- The inhibition of growth rate was 5.4 % and the inhibition of yield was 18.3 % in the limit test. Therefore exact value of ErC50 and EyC50 could not be calculated and the values of EC are given in the form of a range.
The determination of NOEC value was done by statistical software ToxRat Professional Version 3.2.1
72 hour – ErC50 > 100 mg·L-1 (nominal concentration)
72 hour – EyC50 > 100 mg·L-1 (nominal concentration)
72 hour – NOECr < 1 mg· L-1 (nominal concentration)
72 hour – NOECy < 1 mg· L-1 (nominal concentration) - Executive summary:
The test item, Pigment Red 4, 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 (EU) No.2016/266.
The preliminary test was performed in a range of the test item nominal concentrations 1 – 100 mg·L-1.
The highest inhibition of growth rate was 4.3 % and the highest inhibition of yield was 18.8 % in the preliminary test. Based on low toxicity of the test item found in the preliminary test (measured by growth rate), the limit test was performed subsequently. Only the value of 72 hour – ErC50 is needed for the classification and risk assessment of chemicals.
The concentration of 100 mg·L-1 was tested in the limit test. The inhibition of growth rate was 5.4 % and inhibition of yield was 18.3 %.
The study was performed without the analytical determination of the test item concentrations. The suitable analytical method for the determination of the test item concentration is not available.
The nominal concentrations were used for all evaluations and results.
Test results:
72 hour – ErC50 > 100 mg·L-1 (nominal concentration)
72 hour – EyC50 > 100 mg·L-1 (nominal concentration)
72 hour – NOECr ˂ 1 mg·L-1 (nominal concentration)
72 hour – NOECy ˂ 1 mg·L-1 (nominal concentration)
The determination of NOEC value was done by evaluation of the results from preliminary test using statistical software ToxRat Professional Version 3.2.1.
Reference
Mean cell density - limit test
Nominal concentration mg·L-1 |
Mean cell density in 1 mL |
|||
0 hours |
24 hours |
48 hours |
72 hours |
|
100 |
5000 |
17708 |
75000 |
154167 |
Control |
5000 |
23957 |
86458 |
187500 |
Percentual reduction of mean growth rate and percentual inhibition of mean yield – limit test
Nominal concentration mg·L-1 |
Growth rate |
Yield |
||
Mean growth µ |
Reduction % |
Mean area Y |
Inhibition % |
|
100 |
1.14 |
5.4 |
149167 |
18.3 |
Control |
1.21 |
- |
182500 |
- |
Growth curves and other details on results are in attached file PigRed4_157-19-23_Algae_result tables.pdf
Description of key information
The inhibition of growth rate was 5.4 % and the inhibition of yield was 18.3 % in the limit test. Therefore exact value of ErC50 and EyC50 could not be calculated and the values of EC are given in the form of a range.
The determination of NOEC value was done by statistical software ToxRat Professional Version 3.2.1
72 hour – ErC50 > 100 mg·L-1 (nominal concentration)
72 hour – EyC50 > 100 mg·L-1 (nominal concentration)
72 hour – NOECr < 1 mg· L-1 (nominal concentration)
72 hour – NOECy < 1 mg· L-1 (nominal concentration)
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 100 mg/L
- EC10 or NOEC for freshwater algae:
- 1 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.
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