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EC number: 201-758-7 | CAS number: 87-62-7
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
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- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
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- Water solubility
- Solubility in organic solvents / fat solubility
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- Auto flammability
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- 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
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- Additional physico-chemical information
- Endpoint summary
- Stability
- Biodegradation
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- 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
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- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
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- 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
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well documented publication which meets basic scientific principles
Data source
Reference
- Reference Type:
- publication
- Title:
- The in vivo effect of 2,6-xylidine on induction of micronuclei in mouse bone marrow cells
- Author:
- Parton JW, et al.
- Year:
- 1 988
- Bibliographic source:
- Mutat. Res. 206, 281-283
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The ability of 2 .6-xylidine to produce chromosome breakage and/or spindle malformation in vivo was evaluated by an assessment of the capacity of the compound to induce micronuclei in bone marrow polychromatic erythrocytes.
- GLP compliance:
- no
- Type of assay:
- micronucleus assay
Test material
Reference
- Name:
- Unnamed
- Type:
- Constituent
- Details on test material:
- - Name of test material (as cited in study report): 2,6-xylidine
- Aldrich Chemical Co.. Milwaukee, WI
- no further data
Test animals
- Species:
- mouse
- Strain:
- ICR
- Sex:
- male
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: Harlan - Sprague-Dawley, Indianapolis IN
- Weight at study initiation: 28-32 g
- Assigned to test groups randomly: yes
- Fasting period before study: none
- Housing: groups of 5
- Diet Purma pelleted rodent chow (No . 5002) ad libitum
- Water ad libitum
- Acclimation period: 7 days
ENVIRONMENTAL CONDITIONS
- Temperature (°F): 72
- Humidity (%): 40
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle(s)/solvent(s) used: 10 % acacia
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: 2,6-xylidine was diluted in 10 % acacia
- Duration of treatment / exposure:
- not applicable due to single oral application
- Frequency of treatment:
- single treatment
- Post exposure period:
- 72 hours
Doses / concentrations
- Remarks:
- Doses / Concentrations:
87.5, 175, or 350 mg/kg
Basis:
actual ingested
- No. of animals per sex per dose:
- 5 animals
- Control animals:
- yes
- Positive control(s):
- cyclophosphamide;
- Route of administration: oral (gavage)
- Doses / concentrations: 100 mg/kg
Examinations
- Tissues and cell types examined:
- Bone marrow
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION:
highest dose represents 50 % of the oral LD50
TREATMENT AND SAMPLING TIMES:
24, 48, 72 hours
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- The oral administration of up to 350 mg/kg of 2,6-xylidine did not result in the induction of micronuclei in bone marrow of male ICR mice either at 24, 48 or 72 h after dosing. Furthermore, no decrease in the PCE/NCE ratio observed in any animal treated with the test article. In contrast, the administration of 100 mg/kg cyclophosphamide produced a significant induction of micronucleated PCE and confirmed sensitivity of the system for the identification of genotoxins.
Any other information on results incl. tables
Treatment (mg/kg) | Harvest time (h) | PCE/NCE ratio | MPCE/1000 PCE |
350 | 24 | 0.9 ± 0.1 | 1.6 ± 1.5 |
48 | 1.1 ± 0.4 | 2.2 ± 0.8 | |
72 | 1.1 ± 0.4 | 1.2 ± 1.3 | |
175 | 24 | 0.9 ± 0.5 | 1.2 ± 1.1 |
48 | 1.1 ± 0.2 | 0.8 ± 1.1 | |
72 | 1.5 ± 0.2 | 1.3 ± 1.0 | |
87.5 | 24 | 1.0 ± 0.3 | 0.8 ± 1.1 |
48 | 1.0 ± 0.1 | 1.2 ± 0.8 | |
72 | 1.0 ± 0.6 | 1.3 ± 1.3 | |
control | 24 | 1.0 ± 0.2 | 1.4 ± 0.9 |
48 | 1.0 ± 0.0 | 1.0 ± 0.7 | |
72 | 1.3 ± 0.4 | 0.8 ± 1.1 | |
100 cyclophosphamide | 24 | 1.0 ± 0.5 | 46.2 ± 10.7 |
48 | severe bone marrow toxicity | ||
72 | severe bone marrow |
The negative results obtained in this study are in contrast to the positive findings for the in vitro induction of SCE and chromosome aberrations reported by other authors. Such discordant cytogenetic observations are not unprecedented. In vitro systems do not duplicate the possible detoxification, distribution and excretion mechanisms that exist in vivo which can prevent chemicals from reaching a target population, in this case the bone marrow . The absence of an effect on the PCE/NCE ratio in suggests that 2,6-xylidine or an active metabolite may not have been present in bone marrow in sufficient concentration to induce micronuclei. On the other hand, the high dose in this was equivalent to 50% of the LD50 and this should have been more than adequate to evaluate the intrinsic genotoxic potential of the test compound.
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