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EC number: 201-851-2 | CAS number: 88-68-6
- 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 cell study: DNA damage and/or repair
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 000
- Report date:
- 2000
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- updated and adopted July 21, 1997
- GLP compliance:
- yes
- Type of assay:
- mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- Anthranilamide
- EC Number:
- 201-851-2
- EC Name:
- Anthranilamide
- Cas Number:
- 88-68-6
- Molecular formula:
- C7H8N2O
- IUPAC Name:
- 2-aminobenzamide
- Test material form:
- solid: particulate/powder
- Remarks:
- tan
Constituent 1
- Specific details on test material used for the study:
- purity 100%
Test animals
- Species:
- mouse
- Strain:
- other: Crl:CD-1 (ICR) BR
- Details on species / strain selection:
- This is an outbred strain that maximizes genetic heterogeneity and therefore tends to eliminate strain-specific response to test articles.
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- Only male mice were used because no substantial difference in toxic signs between the sexes was observed in the dose-range finding study.
Comercial diet and water was available ad libitum. The animals were assigned randomly by a computer program to the study dose groups. Animals were dosed based upon tehe individual animal weights, on an acute(one-time only) basis.
the weight variation of teh animals did not exceed ±20% of teh mean weight of each sex.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- Corn oil
- Details on exposure:
- Since no appropriate toxicity dat awere available (e.g same species, strain, same route etc.) a dose-range finding study was performed using the same regimen to be used in themicronucleus assay. A dose range of 200 to 2000 mg/kg (200, 500, 800, 1500, 2000) was tested on both sexes. (Three animals per dose group)
As no substantial difference in toxic signs between the sexes was observed in the dose-range finding study, only male mice were used.
The high dose (1200 mg/kg) was chosen to cause toxicity or depression of the ration of PCEs to normochromatic erythrocytes (NCEs). Six animals per dose group were tested, vehicle and positive controls and also a secondary (replacement) dose group of six animals at the high doselevel to be used as substitutes for any deaths. - Duration of treatment / exposure:
- One-time only dosing.
- Frequency of treatment:
- One-time only dosing.
- Post exposure period:
- Harvest times of approximately 24 and 48 hours were used for the high dose and the vehicle control animals. The mid- and low-dose groups, as well as the positive control animals, were harvested approximately 24 hours after treatment.
Doses / concentrationsopen allclose all
- Dose / conc.:
- 300 mg/kg bw (total dose)
- Dose / conc.:
- 600 mg/kg bw (total dose)
- Dose / conc.:
- 1 200 mg/kg bw (total dose)
- No. of animals per sex per dose:
- 6
- Control animals:
- yes, concurrent vehicle
- other: replacement animals at high-dose to substitute any deaths
- Positive control(s):
- cyclophosphamide
Examinations
- Tissues and cell types examined:
- bone marrow, erythrocytes
- Details of tissue and slide preparation:
- After euthanisation, the hind limb bines were removed for marrow extraction from teh first five surviving animals. For each animal, the marrow flushed from teh bones was combined in an individual centrifuge tube containing 3 to 5 mL fetal bovine serum.
Following centrifugsation to pellet the bone marrow tissue,the supernatants were removed by aspiration and portions of teh pellets were spread on lsides and air dried. The slides were fixed in methanol, stained in May-Grunwald solution followed by Giemsa, and protected by mounting with overclips. - Evaluation criteria:
- Slides prepared from the bone marrow were scored for micronucleated PCEs and PCE:NCE cell ratio. The micronucleus frequency was determined by analyzing the number of micronucleated PCEs from 2000 PCEs per animal. The PCE:NCE ration was determined by scoring teh number of PCEs and NCEs observed in the optic fields while scoring at least teh first 200 erythoricytes on the slide.
- Statistics:
- Analysis of variance on untrasnformed proportions of cells with micronuclei per animal and on untrasnformed PCE:NCE ratios when teh variances were homogeneous. Ranked proportions were used for heterogeneous variances.
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- yes
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
Applicant's summary and conclusion
- Conclusions:
- Anthranilamide was found negative in an OECD 474 study in the Mouse, administered by oral gavage conducted under GLP conditions.
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