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EC number: 293-173-9 | CAS number: 91052-16-3
- 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:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 22 Aug 2007 - 21 Sep 2007
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: GLP - Guideline study
- Justification for type of information:
- refer to category justification report provided in IUCLID section 13
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 008
- Report date:
- 2008
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 OTS 798.5395 (In Vivo Mammalian Cytogenics Tests: Erythrocyte Micronucleus Assay)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- THE DEPARTMENT OF HEALTH OF THE GOVERNMENT OF THE UNITED KINGDOM, London, UK
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 736150-63-3
- EC Number:
- 616-005-1
- Cas Number:
- 736150-63-3
- Molecular formula:
- C25H46 O6; C27H48O8
- IUPAC Name:
- 736150-63-3
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- other: Crl:CD1TM (ICR)BR (sufficient albino)
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River (UK) Limited, Margate, Kent, UK
- Age at study initiation: 5 - 8 weeks
- Weight at study initiation: 23 - 30 g
- Assigned to test groups randomly: yes
- Housing: up to 7 animals per cage in solid-floor polypropylene cages with wood-flake bedding
- Diet: Certified Rat and Mouse Diet Code 5LF2, IPS Ltd., London, UK, ad libitum
- Water: ad libitum
- Acclimation period: at least 7 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 - 25
- Humidity (%): 30 - 70
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): 12 / 12
IN-LIFE DATES: From: 12 Sep 2007 To: 14 Sep 2007
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: arachis oil
- Lot/batch no.: P72
- Concentration of test material in vehicle: 2000 mg/kg bw
- Amount of vehicle: 10 mL/kg bw - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
The dosing solution was prepared freshly by dissolving appropriate amounts of the test material in arachis oil yielding a suspension with the final concentration of 2000 mg/kg bw. - Duration of treatment / exposure:
- 24 and 48 h (vehicle control and dose group)
24 h (positive control group) - Frequency of treatment:
- single treatment
- Post exposure period:
- 24 and 48 h (vehicle control and dose group)
24 h (positive control group)
Doses / concentrations
- Remarks:
- Doses / Concentrations:
2000 mg/kg bw
Basis:
- No. of animals per sex per dose:
- 7 (vehicle control and dose group), 5 (positive control)
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide
- Route of administration: oral
- Doses / concentrations: 50 mg/kg bw
Examinations
- Tissues and cell types examined:
- Tissue: bone marrow
Cell type: polychromatic and normochromatic erythrocytes - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: Range finding study performed to find the maximum tolerated dose
DETAILS OF SLIDE PREPARATION: Slides were fixed with methanol and stained with May-Grünwald/Giemsa solution.
METHOD OF ANALYSIS: Slides were examined blind using a light microscope at 1000 fold magnification. The incidence of micronucleated cells per 2000 polychromatic erythrocytes was scored per animal. In addition, the number of normochromatic erythrocytes was evaluated per 1000 erythrocytes which were also scored for the evaluation of the incidence of micronuclei.
The ratio of polychromatic and normochromatic erythrocytes was calculated. - Evaluation criteria:
- For the analyses, the number of micronucleated polychromatic erythrocytes was compared between the test group and the vehicle control group.
MUTAGENICITY
A response would be considered as mutagenic when a statistically significant, toxicologically relevant increase in the number of micronucleated polychromatic erythrocytes was observed for either the 24 or 48 h exposure times in regard to the respective vehicle control.
If these criteria were not met, the test substance was considered as non-mutagenic under the applied test conditions.
CYTOTOXICITY
Bone marrow toxicity was considered when the polychromatic to normochromatic ratio was statistically significantly lower in the dose group than in the concurrent vehicle control group. - Statistics:
- Mean values and standard deviations were calculated. Statistical analyses were performed by Student´s t test (two-tailed) after √(x + 1) transformation. Any significant result was confirmed via One-Way Analysis of Variance.
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 1000 - 2000 mg/kg bw
- Clinical signs of toxicity in test animals: No clinical signs of overt toxicity or mortalities were observed in orally or intraperitoneally exposed animals.
- Other: No marked differences in toxicity were observed in male and female animals.
No evidence of toxicity was observed in animals dosed with the test material via the oral route. Therefore, systemic absorption cannot be confirmed using this dose route.
With no evidence of toxicity being observed in male or female animals dosed with the maximum recommended dose level of 2000 mg/kg bw via the oral and intraperitoneal route, it was considered appropriate to use the intraperitoneal route in the main test to maximize test material exposure and to use male animals only for the main test.
Any other information on results incl. tables
Table 1: Results of the in vivo micornucleus assay in male animals
Treatment group |
Number of animals |
PCE/NCE ratio at sampling time |
|
Total micronuclei per 2000 PCEs at sampling time |
|
24 h |
48 h |
24 h |
48 h |
||
Vehicle control (arachis oil) |
7 |
0.77 ± 0.2 |
0.91 ± 0.42 |
0.7 ± 0.5 |
1.1 ± 1.2 |
Test item (2000 mg/kg bw) |
7 |
0.71 ± 0.26 |
0.93 ± 0.41 |
0.6 ± 0.8 |
0.3 ± 0.5 |
Cyclophosphamide (50 mg/kg bw) |
5 |
1.23 ± 0.26 |
|
51.8 ± 15.7*** |
|
PCE: polychromatic erythrocytes
NCE: normochromatic erythrocytes
***: p < 0.001
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
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