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EC number: 619-447-3 | CAS number: 99607-70-2
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 22 December 1986 to 03 September 1987
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 987
- Report date:
- 1987
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- a top dose level of 2500 mg/kg was used, 1000 PCE were examined per animal
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- heptan-2-yl [(5-chloroquinolin-8-yl)oxy]acetate
- EC Number:
- 619-447-3
- Cas Number:
- 99607-70-2
- Molecular formula:
- C18H22ClNO3
- IUPAC Name:
- heptan-2-yl [(5-chloroquinolin-8-yl)oxy]acetate
- Details on test material:
- - Name of test material (as cited in study report): CGA185072 tech.
- Purity: 91.6%
- Stability: confirmed
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:
- TEST ANIMALS
- Age at study initiation: 4-9 weeks (males), 6-10 weeks (females)
- Weight at study initiation: 22 to 34 g
- Assigned to test groups randomly: yes, by computer generated random numbers
- Housing: individual caging
- Diet: standard diet ad libitum
- Water: ad libitum
- Acclimation period: 4-5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 21°C
- Humidity: 52-66%
- Air changes: air conditioned room
- Photoperiod: 12 hrs dark / 12 hrs light
IN-LIFE DATES: From: 22 December 1986 To: 03 September 1987
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- 0.5% CMC
- Details on exposure:
- Tolerability test: 2500 mg/kg bw, administered to 2 males + 2 females.
Main study: 625,1250, 2500 mg/kg bw (no mortality occurred in the toxicity test at 2500 mg/kg)
Control groups were treated with 0.5% CMC and the positive controls cyclophosphamide, 64 mg/kg bw.
The mutagenicity study was conducted in 8 male and 8 female hamsters per dose group and sampling time. In addition to the treated groups, negative and positive control groups were used. They received the vehicle (0.5% CMC) or the mutagen cyclophosphamide (CPA, 64 mg/kg). - Duration of treatment / exposure:
- Single dose
- Frequency of treatment:
- Once
- Post exposure period:
- 16, 24 or 48 hours
Doses / concentrationsopen allclose all
- Dose / conc.:
- 625 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 250 mg/kg bw/day (nominal)
- Dose / conc.:
- 2 500 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 8 males and 8 females
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- - cyclophosphamide
- Route of administration: oral
- Doses / concentrations: 64 mg/kg bw
Examinations
- Tissues and cell types examined:
- Bone marrow smears were prepared from the shafts of both femurs. After staining, coded slides of 5 animals/sex/dose were scored. 1000 polychromatic erythrocytes per animal were scored for the incidence of micronuclei. The ratio of polychromatic to normochromatic erythrocytes was determined for each animal.
- Details of tissue and slide preparation:
- - Bone marrow smears were prepared from the shafts of both femurs.
- After staining, coded slides of 5 animals/sex/dose were scored. - Evaluation criteria:
- The test substance is considered active if a statistically significant increase in the number of polychromatic erythrocytes with micronuclei in comparison with the negative control occurs at any dose and sampling time.
- Statistics:
- The significance of differences was assessed by the chi square test.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- - No mortality occurred
- Micronucleus test: There was no significant increase of micronuclei. The positive control substance yielded clearly enhanced incidences of polynucleated erythrocytes.
Any other information on results incl. tables
Table 1: Percentage of micronucleated PCE's at different preparation times
Compound and concentration |
Sex |
16 hours |
24 hours |
48 hours |
Test article CGA185072 (625 mg/kg) |
males females |
0.04 |
||
Test article CGA185072 (1250 mg/kg) |
males females |
0.02 |
||
Test article CGA185072 (2500 mg/kg) |
males females |
0.06 0.08 |
0.04 0.12 |
0.04 0.16 |
Negative control Vehicle (0.5% CMC) |
males females |
0.06 0.08 |
0.02 0.08 |
0.06 0.04 |
Positive control Cyclophosphamide (64 mg/kg) |
males females |
4.54 4.22 |
Applicant's summary and conclusion
- Conclusions:
- negative
- Executive summary:
The genotoxicity of cloquintocet-mexyl was studied under GLP to OECD TG 474 in an in vivo micronucleus assay using Chinese hamsters. Dose levels of 625, 1250 and 2500 mg/kg were orally administered. Animals were killed 16, 24 or 48 hours after dosing and bone marrow smears prepared from each femur. After staining the smears, slides from 5 animals/sex/dose were scored for 1000 polychromatic erythrocytes per animal. The number of micronuclei were assessed. Under the conditions of this test there were no clastogenic or aneugenic effects.
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