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EC number: 619-372-6 | CAS number: 98730-04-2
- 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:
- 03 March 1986 to 22 September 1986
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP compliant, guideline study, available as unpublished report, no restrictions, fully adequate for assessment
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 986
- Report date:
- 1986
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Two part main experiment: In the first part a single dose of 5000 mg/kg was administered to 3 groups of 8 male and 8 female Chinese hamsters. The groups were killed after 16, 24, and 48 hours. Three same sized negative control groups were treated with the vehicle and also killed after 16, 24, or 48 hours. The sensitivity of the test system was checked by treating one further group with 64 mg/kg of the known mutagen Cyclophosphamide (CPA). The animals of this group were killed 24 hours after treatment. Analytical purity: 93.9%
In the second part three groups of 8 male and 8 female hamsters were treated with a single dose of 1250, 2500, or 5000 mg/kg of CGA 154281 and killed after 24 hours. Negative and positive control groups were used. After sacrifice the bone marrow from the shafts of both femurs was removed and smears were prepared on slides. Routinely the slides of five animals/sex/dose were stained with May-Grunwald solution and scored for micronuclei. As an exception, the slides from 3 males and 7 females which were killed after 16 hours (part 1) were scored, since only three males in each group furnished well differentiated cells. From each animal the ratio of polychromatic to normochromatic erythrocytes was determined as an indicator for toxic effects on the erythropoiesis and 1000 polychromatic erythrocytes were scored for micronuclei. - GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 2,2-dichloro-1-[(3R)-3-methyl-3,4-dihydro-2H-1,4-benzoxazin-4-yl]ethan-1-one; 2,2-dichloro-1-[(3S)-3-methyl-3,4-dihydro-2H-1,4-benzoxazin-4-yl]ethan-1-one
- EC Number:
- 619-372-6
- Cas Number:
- 98730-04-2
- Molecular formula:
- C11H11Cl2NO2
- IUPAC Name:
- 2,2-dichloro-1-[(3R)-3-methyl-3,4-dihydro-2H-1,4-benzoxazin-4-yl]ethan-1-one; 2,2-dichloro-1-[(3S)-3-methyl-3,4-dihydro-2H-1,4-benzoxazin-4-yl]ethan-1-one
Constituent 1
Test animals
- Species:
- hamster, Chinese
- Strain:
- other: Random outbred strain
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- 3 groups each consisting of 8 male and 8 female Chinese hamsters.
TEST ANIMALS
- Age at study initiation: females 6-10 weeks, males 4-9 weeks
- Weight at study initiation: females 22-32 g, males 20-35 g
- Diet: NAFAG No.924
- Water: Tap water ad libitum
- Acclimation period: 4-5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 22-23°C
- Humidity: 52-59%
- Photoperiod: 12 hrs dark / 12 hrs light
IN-LIFE DATES: From: 03 March 1986 To: 22 September 1986
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- 0.5% aqueous carboxymethylcellulose (CMC).
- Details on exposure:
- Part 1: The different groups of animals were killed after 16, 24, and 48 hours.
Part 2: The different groups of animals were killed after 24 hours. - Duration of treatment / exposure:
- 16 to 48 hours
- Frequency of treatment:
- Single dose
- Post exposure period:
- None.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
1250, 2500 or 5000 mg/kg
Basis:
nominal conc.
- No. of animals per sex per dose:
- 8
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide (CPA)
- Route of administration: oral gavage
- Doses / concentrations: 64 mg/kg
Examinations
- Tissues and cell types examined:
- After sacrifice the bone marrow from the shafts of both femurs was removed and smears were prepared on slides.
- Details of tissue and slide preparation:
- Routinely the slides of five animals/sex/dose were stained with May-Grunwald solution and scored for micronuclei. As an exception, the slides from 3 males and 7 females which were killed after 16 hours (part 1) were scored, since only three males in each group furnished well differentiated cells.
- Evaluation criteria:
- From each animal the ratio of polychromatic to normochromatic erythrocytes was determined as an indicator for toxic effects on the erythropoiesis and 1000 polychromatic erythrocytes were scored for micronuclei.
- Statistics:
- Chi-Square test used
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- In both parts of the main experiment all hamsters survived. At all sampling times (16, 24, and 48 hours) and at all dose levels (5000, 2500, and 1250 mg/kg) no statistically significant increase of micronucleated polychromatic erythrocytes (PCEs) was observed when compared to the negative control. In the positive control groups the percentage of micronucleated PCEs was statistically significant increased, thus demonstrating the sensitivity of the test system.
Any other information on results incl. tables
Chinese hamster micronucleus test |
||||
Part 1: Percentage of micronucleated PCEs at different preparation times |
||||
Test article and concentration |
Sex |
16 hours |
24 hours |
48 hours |
CGA154281 (5000 mg/kg) |
males females mean |
0.07 0.06 0.06 |
0.00 0.08 0.04 |
0.06 0.06 0.06 |
Negative control – vehicle (0.5% CMC) |
males females mean |
0.07 0.04 0.05 |
0.04 0.04 0.04 |
0.10 0.04 0.07 |
Positive control – cyclophoshamide (64 mg/kg) |
males females mean |
|
3.68 5.46 4.57* |
|
* p>0.05 (Chi-Square test) |
Chinese hamster micronucleus test |
|||||
Part 2: Percentage of micronucleated PCEs at different dose levels sacrificed after 24 hours |
|||||
Sex |
CGA154281 1250 mg/kg |
CGA154281 2500 mg/kg |
CGA154281 5000 mg/kg |
Negative control 0.5% CMC |
Positive control 64 mg/kg CPA |
Males Females Mean |
0.02 0.00 0.01 |
0.04 0.02 0.03 |
0.04 0.06 0.05 |
0.08 0.02 0.05 |
2.00 1.58 1.79* |
* p > 0.05 (Chi-Square Test) |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
Under the given experimental conditions no evidence for a clastogenic or aneugenic activity of CGA154281 was observed in vivo. - Executive summary:
CGA154281 technical, Benoxacor, was administered by gavage to Chinese hamsters to evaluate any mutagenic activity on polychromatic erythrocytes in bone marrow cells, in vivo. In the first experiment the highest dose of 5000 mg/kg was administered and animals sacrificed 16, 24 or 48 hours later. In the second assay, doses of 1250, 2500 and 5000 mg/kg were administered and animals sacrificed after 24 hours exposure.
In the first assay, bone marrow smears showed no significant increase in micronucleated polychromatic erythrocytes.
In the second assay, bone marrow smears showed no significant increase in micronucleated polychromatic erythrocytes.
No evidence of mutagenic effects were found in the Chinese hamster after oral administration of Benoxacor.
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