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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
Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 30.09. to 23.10.2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 211 (Daphnia magna Reproduction Test)
- Version / remarks:
- Adopted: October 2, 2012
- Deviations:
- yes
- Remarks:
- with no impact on proper study performance and study results (see Any other information)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.20 (Daphnia magna Reproduction Test)
- Version / remarks:
- Council Regulation (EU) No. 2017/735, published in O.J. L 112, 2017
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
Because the test item is poorly soluble, the test solutions (1, 5 and 10 mg·L-1) were prepared by direct weighing the test item into a graduated flask. The test solutions were ultrasonicated for 30 minutes and then were stirred for 1 hours. After the period of stirring the test solutions were filtered through 0.45 μm filter and these solutions were used for testing.
The stock solutions of the M4 medium were prepared by adding measured amounts of the individual chemicals to deionized water.
The concentration of the test item in M4 medium were prepared three times a week for the preliminary test. The frequency of test solutions renewal was three times per week, without aeration. Fresh test solutions were prepared and parent animals were transferred to them by glass pipette.
Control test was performed concurrently with M4 medium only. The volume of the test solutions was 100 mL in each test beaker. 10 pieces of daphnia were put individually into each test concentration and control series.
Preliminary test: 10, 5, 1, 0 mg·L-1
Definitive test: Based on no toxicity of the test item found in the preliminary test, the study was terminated. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
Daphnia magna Straus
- Source, method: aperiodic parthenogenesis from own laboratory breeding
The grow-up gravid females are separated into M4 medium. Young daphnia born in 24 hours are segregated by observation under a microscope. Only the females are transferred to the test containers.
- Feeding during test, type, amount, frequency: daily (out of 05.10., 06.10., 12.10., 13.10., 19.10., 20.10.), the mixture of two algae (Desmodesmus subspicatus and Raphidocelis subcapitata 1:1), ration levels 0.5 mg C/daphnia/day at all times
Volume of the mixture of algae for feeding: 477 µL/100 mL in preliminary test - Test type:
- semi-static
- Water media type:
- freshwater
- Remarks:
- The stock solutions of the M4 medium were prepared by adding measured amounts of the individual chemicals to deionized water.
- Limit test:
- no
- Total exposure duration:
- 21 d
- Post exposure observation period:
- none
- Hardness:
- above 2.4 mmol·L-1
Preliminary test: 2.42 – 2.47 mmol Ca+Mg /L - Test temperature:
- 20 ± 2°C, with a variation of ± 2°C at each individual test
- pH:
- 6 – 9 and should not change more than 1.5 pH unit
Preliminary test: 8.1 - 8.5 - Dissolved oxygen:
- higher than 3 mg·L-1
Preliminary test: 7.2 – 7.9 - Salinity:
- n.a.
- Conductivity:
- Preliminary test: 1.39 – 2.73 µS·cm-1
- Nominal and measured concentrations:
- Preliminary test: 10, 5, 1 mg·L-1
- Details on test conditions:
- TEST SYSTEM
- Material, size, headspace, fill volume: 100 ml
- Aeration: without
- Renewal rate of test solution (frequency/flow rate): 3× per week
- No. of organisms per vessel: 1
- No. of vessels per concentration (replicates): 10
- No. of vessels per control (replicates): 10
- Volume of the mixture of algae for feeding: 477 µL/100 mL in preliminary test
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: deionized water
- Test medium: M4
- Conductivity of the deionized water: preliminary test: 1.39 – 2.73 µS·cm-1
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 hours light
- Light intensity: 1568 – 1575 lx (not exceeding 1250 – 1670 lx in general) - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Key result
- Duration:
- 21 d
- Dose descriptor:
- EC50
- Effect conc.:
- > 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Details on results:
- The following data were recorded during the test: numbers of living offspring by each parent animal, presence of dead offspring and mortality parent animals. The total number of offspring per parent animal was calculated for each test vessel. If in any test vessel the parent animal died during the test, then the test vessel was excluded from the analysis.
The mean reproductive output for each concentration and control were calculated. Reduction of reproductive output was expressed in %.
- Mortality of control: 0 parent animal; 0 offspring
- Results with reference substance (positive control):
- a) Reference test
The sensitivity of the test species and correctness of test performance is periodically verified by testing with the reference substance, potassium dichromate. The results of the verification test with K2Cr2O7 are the following:
21 days – EC50 = 0.26 mg/L (95% confidence limit: 0.25 – 0.27 mg/L)
b) Data in the literature
HERMENS, JOOP, et al. Joint effects of a mixture of 14 chemicals on mortality and inhibition of reproduction of Daphnia magna. Aquatic Toxicology, Volume 5, Issue 4, November 1984, Pages 315-322.
21 days – EC50 = 0.27 mg/L
c) Method validity evaluation
The reduction in reproductive output of the test organism by the reference substance (21d – EC50) obtained from our reference test is conformable to the values stated in the literature (Hermens et al., 1984). - Validity criteria fulfilled:
- yes
- Remarks:
- see Overall remarks
- Conclusions:
- The observed reduction in reproductive output of Daphnia was 1.5 % in the highest concentration in the preliminary test. Therefore exact values of EC50 could not be calculated and the values of EC are given in the form of a range. The nominal concentrations of the test item were used for all evaluations and results.
Preliminary test showed that it could be reasonable to expect that estimated EC50 will be higher than 10 mg·L-1:
21 days – EC50 > 10 mg/L
In congruence with study plan, when the assumed value of EC50 is higher than 10 mg·L-1, no further testing is needed and the result obtained in preliminary test presents the result of whole study.
Definitive test was not needed, because no effect was observed at the highest concentration in the preliminary test and arrangement of preliminary test meets conditions specified in guideline for limit test (ten replicates for both the treatment and control groups and the timelines is 21 days). - Executive summary:
The test item, Pigment Red 4, was tested in reproduction test on Daphnia magna.
The test was performed according OECD Test Guideline No. 211 - Daphnia magna Reproduction Test. Adopted: October 2, 2012.
The test item is poorly soluble substance, the test solutions were prepared by direct weighing the test item into a graduated flask with M4 medium. The test solutions were ultrasonicated for 30 minutes and then were stirred for 1 hours. After the period of stirring the test solutions were filtered through 0.45 μm filter.
The preliminary test was performed in a range of the test item concentration 1 – 10 mg·L-1. The test was performed as semi-static, frequency of the test solutions renewal was three times a week.
The calculated reduction in reproductive output was 1.5 % in the highest concentration, the exact values of EC50 could not be calculated on the basis of data acquired. Test result is given in the form of a range. In congruence with study plan, when the assumed value of EC50 is higher than 10 mg·L-1, no further testing is needed and the result obtained in preliminary test presents the result of whole study.
The experiment with the concentration of 10 mg·L-1 included in the preliminary test has been performed using ten replicates for both the treatment and the control groups, therethrough the conditions of the limit test given in guideline have been fulfilled and no further testing was needed.
The study was performed without analytical determination of the test item concentrations. The suitable analytical method for the determination of the test item concentration was not available.
For all evaluations and results the nominal concentrations of the test item were used.
Test results, based on nominal concentration:
21 days – EC50 > 10 mg/L
Reference
The total number of living and dead daphnia
Concentration mg·L-1 |
Living offspring Total |
Living offspring of survived parents |
Dead parent animals |
Dead offspring Total |
10 |
597 |
597 |
0 |
0 |
5 |
579 |
579 |
0 |
0 |
1 |
593 |
593 |
0 |
0 |
K |
606 |
606 |
0 |
0 |
The evaluation of reduction in reproductive output of daphnia
Concentration mg·L-1 |
The mean number |
Reduction in reproductive output versus control % |
10 |
59.7 |
1.5 % |
5 |
57.9 |
4.5 % |
1 |
59.3 |
2.1 % |
K |
60.6 |
- |
Detailed information on offspring per individual replicate or concentration-response curve are provided by file in section Attached background material.
Description of key information
The observed reduction in reproductive output of Daphnia was 1.5 % in the highest concentration in the preliminary test. Therefore exact values of EC50 could not be calculated and the values of EC are given in the form of a range. The nominal concentrations of the test item were used for all evaluations and results.
Preliminary test showed that it could be reasonable to expect that estimated EC50 will be higher than 10 mg·L-1:
21 days – EC50 > 10 mg/L
In congruence with study plan, when the assumed value of EC50 is higher than 10 mg·L-1, no further testing is needed and the result obtained in preliminary test presents the result of whole study.
Definitive test was not needed, because no effect was observed at the highest concentration in the preliminary test and arrangement of preliminary test meets conditions specified in guideline for limit test (ten replicates for both the treatment and control groups and the timelines is 21 days).
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 10 mg/L
Additional information
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