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EC number: 700-345-3 | CAS number: 515851-08-8
- 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
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: guideline study and GLP
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 005
- Report date:
- 2005
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- not specified
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- N4-[3-(1H-imidazol-1-yl)propyl]-2-methylbenzene-1,4-diamine trihydrochloride
- EC Number:
- 700-345-3
- Cas Number:
- 515851-08-8
- Molecular formula:
- C13H21Cl3N4
- IUPAC Name:
- N4-[3-(1H-imidazol-1-yl)propyl]-2-methylbenzene-1,4-diamine trihydrochloride
- Reference substance name:
- [TN]Kn 172[/TN][SPEC][/SPEC][AM]99%[/AM]
- IUPAC Name:
- [TN]Kn 172[/TN][SPEC][/SPEC][AM]99%[/AM]
- Details on test material:
- Kn 172
Constituent 1
Constituent 2
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male/female
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- physiol. saline
- Duration of treatment / exposure:
- 24, 48 hours
- Frequency of treatment:
- single
Doses / concentrations
- Remarks:
- Doses / Concentrations:
7.5, 15, 30 mg/kg bw
Basis:
other: vehicle and 50 mg/kg body weight of cyclophosphamide (CP), respectively
- No. of animals per sex per dose:
- 5
- Control animals:
- yes
- Positive control(s):
- The positive control used in the micronucleus test was cyclophosphamide (CAS no.
50-1 8-0; Endoxan) dissolved in physiological saline
dosed as a single intraperitoneal injection of 50 mglkg body weight.
Examinations
- Evaluation criteria:
- Equivocal results should be clarified by further testing using modification of experimental
conditions.
A test substance is considered positive in the micronucleus test if:
- It induced a biologically as well as a statistically significant (Wilcoxon Rank Sum Test; twosided
test at P 0.05) increase in the frequency of rnicronucleated polychromatic
erythrocytes (at any dose or at any sampling time) in the combined data for both sexes or in
the data for male or fernale groups separately.
A test substance is considered negative in the micronucleus test if:
- None of the tested concentrations or sampling times showed a statistically significant (P
0.05) increase in the incidence of micronucleated polychromatic erythrocytes neither in the
combined data for both sexes nor in the data for male or female groups separately.
The preceding criteria are not absolute and other modifying factors may enter into the final
evaluation decision.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- The number of micronucleated polychromatic erythrocytes was counted in 2000 polychromatic
erythrocytes. The ratio polychromatic to normochromatic erythrocytes was determined by
counting and differentiating the first 1000 erythrocytes at the same time. Micronuclei were only
counted in polychromatic erythrocytes. Averages and standard deviations were calculated.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
It is concluded that this test is valid and that Kn 172 is not mutagenic in the micronucleus test
under the experimental conditions described in this report. - Executive summary:
Micronucleus test in bone marrow cells of the mouse with Kn 172.
Kn 172 was tested in the Micronucleus Test in mice, to evaluate its genotoxic effect on
erythrocytes in bone marrow.
The study procedures described in this report were based on the most recent OECD and EEC
guidelines.
Batch Kn-Gi 863411 of Kn 172 was a white powder with a purity of >99%. The test substance
was dissolved in physiological saline.
Five male and five fernale anirnals were used in each of the six treatment groups, including
negative and positive controls. All groups received a single intraperitoneal injection. The
negative and positive control groups were treated with vehicle and 50 rnglkg body weight of
cyclophosphamide (CP), respectively. Animals were dosed with Kn 172 at 30 (two groups), 15
(one group), and 7.5 (one group) mglkg body weight. Additional animals were dosed with the
highest dose level to compensate for possible deaths. After dosing the animals of the dose level
of 30 mglkg body weight showed the following toxic signs: lethargy, hunched posture, rough
coat (1 7 male anirnals and 12 female anirnals) and ptosis (4 male animals and one female
animal). Animals dosed with 15 mg Kn 172lkg body weight showed the following toxic signs:
rough coat (all male animals) and hunched posture (all male and 3 female animals). The
animals of the dose level of 7.5 rnglkg body weight showed no abnorrnalities after dosing.
Bone rnarrow of the groups treated with Kn 172 was sampled 24 or 48 (highest dose only) hours
after dosing. Bone rnarrow of the negative and positive control groups was harvested 24 and 48
hours after dosing, respectively.
Additional animals (three animals per time point) were dosed with 30 mg Kn 1721kg body weight
or with vehicle for blood sampling. Blood was sampled one and four hours after dosing of the
animals of the highest dose group. Blood from the vehicle control animals was sampled one
hour after dosing.
No increase in the mean frequency of rnicronucleated polychromatic erythrocytes was observed
in the polychrornatic erythrocytes of the bone rnarrow of anirnals treated with Kn 172.
The incidence of micronucleated polychromatic erythrocytes in the bone rnarrow of all negative
control animals was within the historical solvent control data range. Cyclophosphamide, the
positive control substance, induced a statistically significant increase in the number of
micronucleated polychromatic erythrocytes in both Sexes. Hence, both criteria for an acceptable
assay were met.
The groups that were treated with Kn 172 showed no decrease in the ratio of polychrornatic to
normochromatic erythrocytes compared to the vehicle controls, which reflects a lack of toxic
effects of this cornpound on the erythropoiesis. The groups that were treated with
cyclophosphamide showed an expected decrease in the ratio of polychromatic to
normochromatic erythrocytes cornpared to the vehicle controls, demonstrating toxic effects on
erythropoiesis.
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