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EC number: 257-055-0 | CAS number: 51202-86-9
- 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
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- Flash point
- Auto flammability
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- 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
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- 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
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- Endpoint summary
- Stability
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- 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

Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 1998
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Standard guideline study according to GLP
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 998
- Report date:
- 1998
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- C.I. Solvent Yellow 133
- IUPAC Name:
- C.I. Solvent Yellow 133
- Reference substance name:
- Polysynthren-Gelb GG
- IUPAC Name:
- Polysynthren-Gelb GG
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: powder
Constituent 1
Constituent 2
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Winkelmann GmbH Gartenstrasse 27, 33178 Borchen
- Age at study initiation:
- Weight at study initiation:male: 37,1g ; female: 28,5g
- Assigned to test groups randomly: yes
- Housing: groups of 5 in makrolon cage type 3
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 5 d
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22+/-3
- Humidity (%):50+/-20
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- sesame oil
- Details on exposure:
- Animals were treated twice at an interval of 24 hours
- Duration of treatment / exposure:
- 2 days
- Frequency of treatment:
- 1/day for 2 days
- Post exposure period:
- 24 h
Doses / concentrations
- Remarks:
- Doses / Concentrations:
2000 mg/kg
Basis:
actual ingested
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- other: concurrent, positive control
- Positive control(s):
- cyclophosphamide; c
- Route of administration: oral gavage
- Doses / concentrations: 50 mg/kg bw.
Examinations
- Tissues and cell types examined:
- bone marrow from the femur
- Details of tissue and slide preparation:
- Animals were killed by carbon dioxide asphyxiation 24 hours after dosing. For each animal, about 3 ml fetal bovine serum was poured into a centrifuge tube. Both femora were removed and the bones freed of muscle tissue. The proximal ends of the femora were opened and the bone marrow flushed into the centrifuge tube. A suspension was formed. The mixture was then centrifuged for 5 minutes at approx. 1200 rpm, after which almost all the supernatant was discarded. One drop of the thoroughly mixed sediment was smeared onto a cleaned slide, identified by project code and animal number and air-dried for about 12 hours.
Staining was performed as follows:
- 5 minutes in methanol
- 5 minutes in May-Grünwald's solution
- brief rinsing twice in distilled water
- 10 minutes staining in 1 part Giemsa solution to 6 parts buffer solution, pH 7.2 (Weise)
- rinsing in distilled water
- drying
- coating with Entellan - Evaluation criteria:
- Evaluation
2000 polychromatic erythrocytes were counted for each animal. The number of cells with micronuclei was recorded, not the number of individual micronuclei. In addition, the ratio of polychromatic erythrocytes to 200 total erythrocytes was determined. Main parameter for the statistical analysis, i.e. validity assessment of the study and mutagenicity of the test substance, was the proportion of polychromatic erythrocytes with micronuclei out of the 2000 counted erythrocytes. All bone marrow smears for evaluation were coded to ensure that the group from which they were taken remained unknown to the investigator.
A one-sided Wilcoxon-Test (4, 5] was evaluated to check the validity of the study. The study was considered as valid in case the proportion of polychromatic erythrocytes with micronuclei in the positive control was significantly higher than in the negative control (p=0.05).
If the validity of the study had been shown the following sequential test procedure for the examination of the mutagenicity was applied: Based on a monotone-dose-relationship one-sided Wilcoxon tests were performed starting with the highest dose group. These test were performed with a multiple level of significance of 5%.
Criteria for a positive response
Both biological and statistical significances were considered together for evaluation purposes.
A substance is considered positive if there is a significant increase in the number of micronucleated polychromatic erythrocytes compared with the concurrent negative control group. A test substance producing no significant increase in the number of micronucleated polychromatic erythrocytes is considered non-mutagenic in this system.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
Any other information on results incl. tables
Pooled result for both sexes
Dose |
Time |
Animals |
Poly |
Poly/Ery |
Poly/Ery |
Poly with MN |
Poly with MN |
Poly with MN |
Mut. Index |
|
|
|
counted |
Mean |
SD |
mean |
% |
SD |
|
0 (neg Ccontrol) |
|
10 |
2000 |
0,49 |
0,07 |
1,30 |
0,1 |
0,05 |
1,0 |
2000 |
|
10 |
2000 |
0,45 |
0,10 |
1,80 |
0,1 |
0,07 |
1,4 |
50 (pos control) |
|
10 |
2000 |
0,47 |
0,04 |
53,30 |
2,7 |
0,79 |
41,0* |
*=significantly different from control (p<0,05)
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
The test item did not lead to a substantial increase of micronucleated polychromatic erythrocytes and is not mutagenic in the micronucleus test under the conditions described. - Executive summary:
Mice were treated twice with 2000 mg of the test item per kg body weight to study the induction of micronuclei in bone marrow cells. All animals survived after treatment.
No signs of toxicity were observed. The dissection of the animals revealed no test substance related findings.
The bone marrow smears were examined for the occurrence of micronuclei in red blood cells.
The incidence of micronucleated polychromatic erythrocytes in the dose group of the test item was within the normal range of the negative control groups. No statistically significant increase of micronucleated polychromatic erythrocytes was observed.
The ratio of polychromatic erythrocytes to total erythrocytes remained essentially unaffected by the test compound and was not less than 20% of the control values.
Cyclophosphamide (Endoxan®) induced a marked and statistically significant increase in the number of polychromatic erythrocytes with micronuclei, thus indicating the sensitivity of the test system.
CONCLUSION
The results lead to the conclusion that the test item did not lead to a substantial increase of micronucleated polychromatic erythrocytes and is not mutagenic in the micronucleus test under the conditions described in this report.
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