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EC number: 266-257-8 | CAS number: 66215-27-8
- 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:
- supporting study
- Study period:
- 1986/11 to 1987/07
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
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:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- Only 2 dose levels (instead of three) were used; Only 1000 polychromatic erythrocytes (instead of 2000) were analysed for the presence of micronuclei.
- GLP compliance:
- yes
- Type of assay:
- mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- N-cyclopropyl-1,3,5-triazine-2,4,6-triamine
- EC Number:
- 266-257-8
- EC Name:
- N-cyclopropyl-1,3,5-triazine-2,4,6-triamine
- Cas Number:
- 66215-27-8
- Molecular formula:
- C6H10N6
- IUPAC Name:
- N2-cyclopropyl-1,3,5-triazine-2,4,6-triamine
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- Tif:MAGf
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: female 6-10 weeks, male 4-9 weeks
- Weight at study initiation: female 27-31 g, male 33-35 g (tolerability test), female 22-29 g, male 26-36 g (mutagenicity test)
- Water: Tap water ad libitum
- Acclimation period: 4-6 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22-23 °C
- Humidity (%): 41-66 %
- Photoperiod (hrs dark / hrs light): The room was illuminated for 12 hours daily
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- 0.5% CMC
- Frequency of treatment:
- The animals were treated once.
- Post exposure period:
- maximum of 72 hours
Doses / concentrationsopen allclose all
- Dose / conc.:
- 1 080 mg/kg bw/day (nominal)
- Remarks:
- High dose
- Dose / conc.:
- 360 mg/kg bw/day (nominal)
- Remarks:
- Low dose
- No. of animals per sex per dose:
- 8
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide at 64 mg/kg bw.
Examinations
- Tissues and cell types examined:
- Bone marrow cells
- Details of tissue and slide preparation:
- Bone marrow was harvested from the shafts of both femurs with fetal calf serum. After centrifugation small drops of the sediment mixture were transferred on the end of a slide, spread out with the aid of a polished cover glass and the preparations were air-dried. Within 24 hours, the slides were stained in undiluted May-Grunwald solution for 3 min then in May-Grunwald solution/water 1/1 for 2 min. After being rinsed in distilled water, the slides were left immersed in diluted Giemsa solution for 10 min. After rinsing with distilled water and air-drying, the slides were cleared in xylene and mounted.
- Evaluation criteria:
- The test substance was considered to be active in this test system if a statistically significant increase in the number of polychromatic erythrocytes with micronuclei in comparison with the negative control occurred at any dose and sampling time respectively.
- Statistics:
- The significance of difference was assessed by X^2-test.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- not applicable
- Positive controls validity:
- valid
- Additional information on results:
- In the mutagenicity test one male animal of the 1080 mg/kg bw dose group died within the treatment period of 72 hours.
In the mutagenicity test, there was no significant increase in the number of micronucleated polychromatic erythrocytes in the animals treated with the dose of 360 mg/kg bw as well as with the dose of 1080 mg/kg bw as compared with the negative control animals.
By contrast, the positive control (cyclophosphamide) yielded a marked increase of the percentage of micronucleated cells. Here, the mean percentage of polychromatic erythrocytes with micronuclei was 1.99. In comparison with the negative control (0.10%) this value is highly significant (p<0.05).
Any other information on results incl. tables
In a preliminary assay 1080 mg/kg bw was determined to be the maximum tolerated dose.
The results are provided in the table below.
Applicant's summary and conclusion
- Conclusions:
- Cyromazine did not induce any statistically significant increase in MPCE incidence in mice bone marrow cells in vivo up to and including 1080 mg/kg bw (the maximum tolerated dose).
- Executive summary:
In an in vivo Micronucleus study, the test item was administered once by gavage at 1080 or 360 mg/kg bw to male and female mice. The animals were sacrificed 24, 48 and 72 hours after treatment. One male in the high dose group died. The bone marrow smears from treated animals 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 1.99% polychromatic erythrocytes with micronuclei. This is significantly different from the controls treated with the vehicle (0.5% CMC) alone.
It is concluded that under the conditions of this experiment, no evidence of mutagenic effects was obtained in mice treated with the test item.
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