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EC number: 249-204-3 | CAS number: 28768-32-3
- 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:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- from 2012-10-08 to 2013-01-14
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was performed under GLP and according to guidelines
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 013
- Report date:
- 2013
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:
- EU Method B.12 (Mutagenicity - In Vivo Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5395 (In Vivo Mammalian Cytogenetics Tests: Erythrocyte Micronucleus Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: TSCA, FIFRA and Japanese METI/MHLW guidelines
- Deviations:
- no
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 4,4'-Methylenedianiline, oligomeric reaction products with 1-chloro-2,3-epoxypropane
- EC Number:
- 500-062-3
- EC Name:
- 4,4'-Methylenedianiline, oligomeric reaction products with 1-chloro-2,3-epoxypropane
- Cas Number:
- 28390-91-2
- IUPAC Name:
- 4-[(4-aminophenyl)methyl]aniline; 2-(chloromethyl)oxirane
- Test material form:
- liquid: viscous
- Details on test material:
- - Name of test material (as cited in study report): 4,4'-Methylenedianiline, oligomeric reaction products with 1-chloro-2,3-epoxypropane
- Physical state: Amber coloured extremely viscous liquid
- Storage condition of test material: approximately 4 °C, in the dark
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Harlan Laboratories UK Ltd, Oxon, UK
- Age at study initiation: 6-10 weeks old
- Weight at study initiation: 25-30 g
- Assigned to test groups randomly: yes
- Fasting period before study: no data
- Housing: in groups of up to seven in solid-floor polypropylene cageswith wood-flake bedding
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: minimum 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-25
- Humidity (%): 30-70
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: arachis oil
- Justification for choice of solvent/vehicle: no data
- Concentration of test material in vehicle: 50, 100, 200 mg/mL
- Amount of vehicle (if gavage or dermal): 10 mL/kg - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: The test item was freshly prepared as required as an emulsion at the appropriate concentration in arachis oil.
- Duration of treatment / exposure:
- 24 h after dosing of 0, 500, 1000 and 2000 mg/kg test item and 50 mg/kg positive control
48 h after dosing of 2000 mg/kg - Frequency of treatment:
- single treatment
- Post exposure period:
- 24 h after dosing of 0, 500, 1000 and 2000 mg/kg test item and 50 mg/kg positive control
48 h after dosing of 2000 mg/kg
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 50, 1000, 2000 mg/kg
Basis:
actual ingested
- No. of animals per sex per dose:
- 7 male mice per group
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide
- Justification for choice of positive control(s): the item known to produce micronuclei under the conditions of the test
- Route of administration: oral (gavage)
- Doses / concentrations: 50 mg/kg / 5 mg/mL
Examinations
- Tissues and cell types examined:
- bone marrow smears
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields): single treatment and sampling times: 24 or 48 h following dosing
DETAILS OF SLIDE PREPARATION: both femurs were dissected from each animal, aspirated with foetal bovine serum and bone marrow smears prepared following centrifugation and re-suspension. The smears were air-dried, fixed in absolute methanol, stained in May-Grünwald/Giemsa, allowed to air-dry and a cover slip applied using mounting medium.
METHOD OF ANALYSIS: Stained bone marrow smears were coded and examined blind using light microscopy at x1000 magnification. The incidence of micronucleated cells per 2000 polychromatic erythrocytes (PCE-blue stained immature cells) per animal was scored. Micronuclei are normally circular in shape, although occasionally they may be oval or half-moon shaped, and have a sharp contour with even staining. In addition, the number of normochromatic erythrocytes (NCE-pink stained mature cells) associated with 1000 erythrocytes was counted; these cells were also scored for incidence of micronuclei. - Evaluation criteria:
- A positive mutagenic response would be demonstrated when a statistically significant, dose-responsive, toxicologically relevant increase in the number of micronucleated polychromatic erythrocytes was observed for either the 24 or 48-hour kill times when compared to the vehicle control group.
If these criteria were not fulfilled, then the test item would be considered non-genotoxic under the conditions of the test.
A positive response for bone marrow toxicity would be demonstrated when the dose group mean polychromatic to normochromatic ratio was shown to be statistically significantly lower than the vehicle control group. - Statistics:
- The ratio of polychromatic to normochromatic erythrocytes was calculated together with appropriate group mean values and standard deviations. All data were statistically analysed using appropriate statistical methods as recommended by the UKEMS Sub-committee on Guidelines for Mutagenicity Testing Report, Part 111 (1989). The data was analysed following a (x+1)^1/2 transformation using Student's t-test (two tailed) and any significant results were confirmed using the one way analysis of variance.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Remarks:
- at 2000 mg/kg in both the 24 and 48-hour dose groups, a hunched posture and ptosis were observed; A modest but statistically significant decrease in the PCE/NCE ratio was observed in the 48-hour 2000 mg/kg dose when compared to the vehicle control group.
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 2000 mg/kg
- Solubility: an emulsion was prepared
- Clinical signs of toxicity in test animals: at 2000 mg/kg: hunched posture, ataxia and splayed gait
- Evidence of cytotoxicity in tissue analyzed: no data
- Rationale for exposure: It is recommended in the guideline OECD 474 to use the maximum tolerated dose or the highest dose that can be formulated and administered reproducibly or 2000 mg/kg as the upper limit for non-toxic test items.
- Harvest times: no data
- High dose with and without activation: not applicable
RESULTS OF DEFINITIVE STUDY
- Types of structural aberrations for significant dose levels (for Cytogenetic or SCE assay): not applicable
- Induction of micronuclei (for Micronucleus assay): there was no evidence of any statistically significant increases in the incidence of micronucleated polychromatic erytrocytes in animals dosed with the test item when compared to the vehicle control group.
- Ratio of PCE/NCE (for Micronucleus assay): A modest but statistically significant decrease in the PCE/NCE ratio was observed in the 48-hour 2000 mg/kg dose group when compared to the vehicle control group. This decrease, together with the observation of clinical signs, was taken to indicate that systemic absorption had occurred and exposure to the target tissue had been achieved.
- Appropriateness of dose levels and route: the selected dose level at 2000 mg/kg of the test item, i.e. maximum recommended dose, produced some evidence of toxicity wenn administered via the oral route.
- Statistical evaluation: see attached document (Summary results)
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
The test item was considered to be non-mutagenic under the conditions of the test. - Executive summary:
The study was performed to assess the potential of the test item to produce damage to chromosomes or aneuploidy when administered to mice. The method was designed to be compatible with the 1997 OECD Guidelines for Testing of Chemicals No.474 "Mammalian Erythrocyte Micronucleus Test", Method B12 of Commission Regulation (EC) No. 44012008 of 30 May 2008, the US EPA (OPPTS 870.5395), TSCA and FlFRA guidelines, and be acceptable to the Japanese METIIMHLW guidelines for testing of new chemical substances.
A range-finding test was performed to find suitable dose levels of the test item, route of administration, and to investigate if there was a marked difference in toxic response between the sexes. There was no marked difference in toxicity of the test item between the sexes; therefore, the main test was performed using only male mice. Following consultation with the Sponsor, the micronucleus test was conducted using the oral route in groups of seven mice (males) at the maximum recommended dose (MRD) of 2000 mg/kg and with 1000 and 500 mg/kg as the two lower dose levels. Animals were killed 24 or 48 hours later, the bone marrow extracted, and smear preparations made and stained. Polychromatic (PCE) and normochromatic (NCE) erythrocytes were scored for the presence of micronuclei. Additional groups of mice were given a single oral dose of arachis oil (7 male mice) or dosed orally with cyclophosphamide (5 male mice), to serve as vehicle and positive controls respectively. Vehicle and positive control animals were killed after 24 hours.
There were no premature deaths seen in any of the dose groups in the main test. Clinical signs were observed in animals dosed with the test item at 2000 mg/kg in both the 24 and 48-hour dose groups, and included hunched posture and ptosis. A modest but statistically significant decrease in the PCE/NCE ratio was observed in the 48-hour 2000 mg/kg dose group when compared to the vehicle control group. This decrease, together with the observation of clinical signs, was taken to indicate that systemic absorption had occurred and exposure to the target tissue had been achieved. There was no evidence of any statistically significant increases in the incidence of micronucleated polychromatic erythrocytes in animals dosed with the test item when compared to the vehicle control group. The positive control group showed a marked increase in the incidence of micronucleated polychromatic erythrocytes hence confirming the sensitivity of the system to the known mutagenic activity of cyclophosphamide under the conditions of the test. The test item was considered to be non-mutagenic under the conditions of the test.
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