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EC number: 402-860-6 | CAS number: 110553-27-0 CG 25-1320; IRGANOX 1520; TK 12229/1
- 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
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 987
- Report date:
- 1987
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- (only 1000 erythrocytes/animal were counted)
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 4,6-bis(octylthiomethyl)-o-cresol
- EC Number:
- 402-860-6
- EC Name:
- 4,6-bis(octylthiomethyl)-o-cresol
- Cas Number:
- 110553-27-0
- Molecular formula:
- C25 H44 O S2
- IUPAC Name:
- 2-methyl-4,6-bis[(octylsulfanyl)methyl]phenol
- Details on test material:
- - Storage: room temperature
- Physical state: liquid
Constituent 1
Test animals
- Species:
- hamster, Chinese
- Strain:
- not specified
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Ciba Geigy Tierfarm, Sisseln, Switzerland
- Age at study initiation: females 6- 10 weeks, males 4-9 weeks
- Weight at study initiation: females 22-32 g, males 22-34 g
- Diet: ad libitum; Standard diet: NAFAG No.924
- Water: ad libitum
- Acclimation period: 4-5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-21
- Humidity (%): 60-64
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle used: Arachis oil
- Source: Siegfried AG, Switzerland
- Justification for choice of solvent/vehicle: not specified
- Concentration of test material in vehicle:
- Amount of vehicle: 10 ml/kg bw
- Purity: no data - Details on exposure:
- Application volume: 10 ml/kg bw
- Duration of treatment / exposure:
- single dose application
- Frequency of treatment:
- once
- Post exposure period:
- sacrifice was performed 16, 24 and 48 hours after gavage
Doses / concentrations
- Dose / conc.:
- 5 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 8/sex/dose/sampling time
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- - Name: Cyclophosphamide (CPA)
- Source: ASTA-Werke, Germany
- Justification for choice of positive control(s): guideline recommended
- Number of animals: 8/sex/dose/sampling time
- Route of administration: gavage
- Vehicle: Arachis oil
- Application volume: 10 ml/kg bw
- Doses: 64 mg/kg bw
- Time for sacrifice: 24 hours after dosing
Examinations
- Tissues and cell types examined:
- Bone marrow; erythrocytes
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: the dose of 5000 mg/kg was determined as the highest applicable in the mutagenicity assay
DETAILS OF SLIDE PREPARATION: Bone marrow is harvested from the shafts of both femurs with fetal calf serum. After centrifugation small drops of the sediment mixture are transferred on the end of a slide, spread out with the aid of a polished cover glass and the preparations are air-dried. Within 24 hours, the slides are stained in undiluted May-Grünwald solution for 3 min then in May-Grünwald solution/water 1/1 for 2 min. After being rinsed in distilled water, the slides are left immersed in diluted Giemsa solution (16.6%), for 10 min. After rinsing with distilled water and air-drying, the slides are cleared in Xylene and mounted.
METHOD OF ANALYSIS: Prior to analysis the slides are coded. Thereafter the quality of staining is evaluated. The slides of five animals from each sex showing the best differentiation between mature and polychromatic erythrocytes are selected for later scoring. The slides of five female and five male animals each of the negative control group and of the dosage group sacrificed at 16, 24 and 48 hours post treatment are examined. From the animals of the positive control group which are sacrificed 24 hours after application, the slides of five female and five male animals are scored. 1000 polychromatic erythrocytes per animal each are scored for the incidence of micronuclei. The ratio of polychromatic to normochromatic erythrocytes is determined for each animal by counting a total of 1000 erythrocytes. - Statistics:
- The significance of difference is assessed by X^2-test
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose: 200, 1000, 5000 mg/kg bw
- Number of animals/sex/dose: 2 per sex per dose
- Frequency of application: once
- Rationale for exposure: Determine the highest dosage of the test substance to be applied in the mutagenicity assay
- Harvest times: 16, 24, 48 and 72 hours after gavage
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay): There was no significant increase in the number of micronucleated polychromatic erythrocytes in the animals treated with the dose of 5000 mg/kg as compared with the negative control animals.
By contrast, the positive control (cyclophosphamide, 64 mg/kg) yielded a marked increase of the percentage of micronucleated cells. Here the mean percentage of polychromatic erythrocytes with micronuclei was 1.73. In comparison with the vehicle control (0.16) this value is highly significant (p <0.05).
- Percent of polychromatic erythrocytes with micronuclei:
16 h: 0.20 for males (control: 0.20); 0.14 for females (control: 0.10)
24 h: 0.26 for males (control: 0.18); 0.14 for females (control: 0.14)
48 h: 0.30 for males (control: 0.18); 0.04 for females (control: 0.06)
pos. control, 24 h: 2.32 for males (control: 0.18); 1.14 for females (control: 0.14)
- Ratio of PCE/NCE (for Micronucleus assay):
16 h: 1.0 for males; 0.9 for females
24 h: 1.1 for males; 0.9 for females
48 h: 1.1 for males; 1.0 for females
pos. control, 24 h: 1.1 for males; 0.8 for females
Any other information on results incl. tables
SUMMARY OF EXPERIMENTAL RESULTS
Sacrifice | Treatment | Sex | polychromatic erythrocytes (average) |
normochromatic erythrocytes (average) |
ratio of p / n erythrocytes |
number of polychromatic erythrocytes with micronuclei (average) |
% of polychromatic erythrocytes with micronuclei (average) |
16 h | Control | female | 468 | 532 | 0.9 | 2.00 | 0.20 |
male | 453 | 547 | 0.8 | 1.00 | 0.10 | ||
5000 mg/kg | female | 492 | 508 | 1.0 | 2.00 | 0.20 | |
male | 473 | 527 | 0.9 | 1.40 | 0.14 | ||
24 h | Control | female | 484 | 516 | 0.9 | 1.80 | 0.18 |
male | 434 | 566 | 0.8 | 1.40 | 0.14 | ||
5000 mg/kg | female | 520 | 480 | 1.1 | 2.60 | 0.26 | |
male | 460 | 540 | 0.9 | 1.40 | 0.14 | ||
48 h | Control | female | 516 | 484 | 1.1 | 1.80 | 0.18 |
male | 493 | 507 | 1.0 | 0.60 | 0.06 | ||
5000 mg/kg | female | 526 | 474 | 1.1 | 3.00 | 0.30 | |
male | 490 | 510 | 1.0 | 0.40 | 0.04 | ||
Positive Control | |||||||
48 h | Control | female | 484 | 516 | 0.9 | 1.80 | 0.18 |
male | 434 | 566 | 0.8 | 1.40 | 0.14 | ||
64 mg/kg | female | 514 | 486 | 1.1 | 23.20 | 2.32 | |
male | 442 | 558 | 0.8 | 11.40 | 1.14 |
Applicant's summary and conclusion
- Conclusions:
- Under the conditions of this experiment, no evidence of mutagenic effects was obtained in Chinese hamsters treated with the test item.
- Executive summary:
An in vivo micronucleus assay was performed to evaluate any mutagenic effect on polychromatic erythrocytes in bone marrow cells in vivo. Mutagenic effects present themselves in form of micronuclei in polychromatic erythrocytes in the bone marrow. These micronuclei are small particles consisting of acentric fragments of chromosomes or entire chromosomes which lag behind at anaphase stage during the mitotic process. After telophase, these fragments may not be included in the nuclei of daughter cells and form single or multiple micronuclei in the cytoplasm. The increase in micronucleated polychromatic erythrocytes shows a clear dose dependency, comparable to the occurrence of chromosome aberrations in metaphase preparations. In this experiment the animals were treated once with the highest applicable dose of 5000 mg/kg and sacrificed 16, 24 and 48 hours thereafter. The test article was administered by gavage. From the bone marrow smears were made.
The bone marrow smears from the animals treated with the dose of 5000 mg/kg of the test item showed no statistically significant increase (p >0.05) in the number of micronucleated polychromatic erythrocytes in comparison with the negative control animals at all three sampling times. The respective "positive control" experiments with cyclophosphamide (64 mg/kg) yielded an average of 1.73% polychromatic erythrocytes with micronuclei. This is significantly different from the controls (0.16%) treated with the vehicle (arachis oil) alone. It is concluded that under the conditions of this experiment, no evidence of mutagenic effects was obtained in Chinese hamsters treated with the test item.
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