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Diss Factsheets
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EC number: - | CAS number: -
- 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
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2008
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 008
- Report date:
- 2008
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Commission Directive 2000/32/EC, Annex 4C
- Version / remarks:
- dated MAy 19, 2000
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 2,2`-[6-(phenylamino)-1,3,5-triazine-2,4-diyl]diphenol
- Cas Number:
- 1248-66-4
- Molecular formula:
- C21H16N4O2
- IUPAC Name:
- 2,2`-[6-(phenylamino)-1,3,5-triazine-2,4-diyl]diphenol
Constituent 1
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
- Age at Start of Acclimatisation: 8 - 10 weeks
- Weight at study initiation: males mean value 37.8 g (SD ± 2.0 g); females mean value 29.6 g (SD ± 2.0 g)
- Assigned to test groups randomly: yes
- Fasting period before study:
- Housing: single in Makrolon Type I, with wire mesh top
- Diet: pelleted standard diet, ad libitum
- Water: tap water, ad libitum
- Acclimation period: minimum 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 3 °C
- Humidity (%): 30 - 70 %
- Photoperiod (hrs dark / hrs light): artificial light 6.00 a.m. - 6.00 p.m.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- 30% DMSO/70% PEG 400
- Details on exposure:
- substance formulated in vehicle
- Duration of treatment / exposure:
- animals received the test item once
- Frequency of treatment:
- once
- Post exposure period:
- 24 h, 48 h
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
2000 mg/kg body weight
Basis:
actual ingested
- Remarks:
- Doses / Concentrations:
1000 mg /Kg body weight
Basis:
actual ingested
- Remarks:
- Doses / Concentrations:
500 mg/kg body weight
Basis:
actual ingested
- No. of animals per sex per dose:
- low dose: 6 females, 6 males
medium dose: 6 females, 6 males
main experiment: 12 females, 12 males - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide, 40 mg/kg b.w; 24 h;
Examinations
- Tissues and cell types examined:
- bone marrow cells; polychromatic erythrocytes; normochromatic erythrocytes
- Details of tissue and slide preparation:
- according guideline
- Evaluation criteria:
- standard
- Statistics:
- nonparametric Mann-Whitney test
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- ruffeled fur within 4 h after treatment with 2000 mg/kg b.w.
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- pre-experiment:
4 animals (2 males, 2 females) treated with 100 mg/kg b.w. did not express any toxic reactions;
4 animals (2 males, 2 females) treated with 1000 mg/kg b.w: : 1 male and 1 female had ruffeled fur within 2 and 6 h;
4 animals (2 males, 2 females) treated with 2000 mg/kg b.w: :2 males, 1 female had ruffeled fur 1 h post-treatment and 2 males and 2 females within 2 and 24 h post-treatment;
Applicant's summary and conclusion
- Conclusions:
- The oral application of the substance to mice did not induce increased micronucleated polychromatic erythrocytes in bone marrow.
- Executive summary:
The test item was assessed in the micronucleus assay for its potential to induce micronuclei in polychromatic erythrocytes (PCE) in the bone marrow of the mouse. The test item was formulated in 30% DMSO / 70% PEG 400, which was also used as vehicle control. The volume administered orally was 10 mL/kg b.w.. 24 h and 48 h after a single administration of the test item the bone marrow cells were collected for micronuclei analysis.
Ten animals (5 males, 5 females) per test group were evaluated for the occurrence of micronuclei. At least 2000 polychromatic erythrocytes (PCEs) per animal were scored for micronuclei.
To describe a cytotoxic effect due to the treatment with the test item the ratio between polychromatic and normochromatic erythrocytes was determined in the same sample and reported as the number of PCEs per 2000 erythrocytes. The following dose levels of the test item were investigated:
24 h preparation interval: 500, 1000, and 2000 mg/kg b.w..
48 h preparation interval: 2000 mg/kg b.w..
As estimated by a pre-experiment 2000 mg test item per kg b.w. (the maximum guideline-recommended dose) was suitable.
The mean number of polychromatic erythrocytes was not decreased after treatment with the test item as compared to the mean value of PCEs of the vehicle control indicating that the test item did not have any cytotoxic properties in the bone marrow.
In comparison to the corresponding vehicle controls there was no statistically significant or biologically relevant enhancement in the frequency of the detected micronuclei at any preparation interval and dose level after administration of the test item. The mean values of micronuclei observed after treatment with test item were below or near to the value of the vehicle control group. 40 mg/kg b.w. cyclophosphamide administered orally was used as positive control which showed a statistically significant increase of induced micronucleus frequency.
In conclusion, it can be stated that during the study described and under the experimental conditions reported, the test item did not induce micronuclei as determined by the micronucleus test in the bone marrow cells of the mouse.
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