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Diss Factsheets
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EC number: 947-748-2 | CAS number: -
- 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:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study with acceptable restrictions (lack of data on test substance)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 995
- Report date:
- 1995
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- (lack of data on test substance)
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 189200-42-8
- Cas Number:
- 189200-42-8
- IUPAC Name:
- 189200-42-8
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories, St. Constant, Quebec, Canada
- Age at study initiation: approximately 9 weeks
- Weight at study initiation: 32.8 - 40.1 g (males); 27.1 - 31.8 g (females)
- Assigned to test groups randomly: yes, by a computer-generated body weight sorting program
- Housing: the animals were housed individually in suspended stainless steel and wire mesh cages with absorbent paper below the cages.
- Diet: Certified Rodent Diet # 5002 (pellets) (PMI Feeds Inc.), ad libitum
- Water: tap water, ad libitum
- Acclimation period: approximately 2 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 - 24
- Humidity (%): 40 - 70
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES:
From: 18 Sep 1995
To: 21 Sep 1995
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- - Vehicle/solvent used: peanut oil
- Justification for choice of solvent/vehicle: The test substance was soluble in peanut oil at the concentrations required for this study.
- Amount of vehicle: ≤ 1 mL/100 g bw - Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: The test substance was thoroughly mixed with the vehicle.
- Duration of treatment / exposure:
- three applications
- Frequency of treatment:
- approximately every 24 h
- Post exposure period:
- 24 h after the last treatment
Doses / concentrationsopen allclose all
- Dose / conc.:
- 500 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 2 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- cyclophosphamide
- Route of administration: oral by gavage
- Dose: 20 mg/kg bw
Examinations
- Tissues and cell types examined:
- Tissue: bone marrow of the femur
Cell type: bone marrow cells - Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: range finding study performed to find the maximum tolerated dose
DETAILS OF SLIDE PREPARATION: 2 slides per animal were prepared. The slides were stained with acridine orange and wet mounted.
METHOD OF ANALYSIS: 2000 polychromatic erythrocytes (PCEs) from each animal were examined for the presence of micronuclei. - Evaluation criteria:
- The test substance may be considered positive in this test system if at least one of the following criteria is met:
- The mean number of the micronucleated PCEs of at least one dose point is statistically different from the mean number of the micronucleated PCEs of the vehicle control. This value also must be outside the normal range of the micronucleated PCEs of the vehicle control. Additionally, a dose related statistical increase in the mean number of micronucleated PCEs must be observed.
- The mean number of the micronucleated PCEs of at least two dose points is statistically different from the mean number of the micronucleated PCEs of the vehicle control. This values also must be outside the normal range of the micronucleated PCEs of the vehicle control. - Statistics:
- The statistical analysis included means and standard deviations of the micronuclei data and a test of equality of group means performed by a standard one-way analysis of variance (ANOVA).
Residuals from the ANOVA were analyzed for normality by either Wilk's Criterion or the Kolomogorov-Smirnov Statistic. If the residuals were not normally distributed (at 0.01 level of significance) in more than 25% of the analyses then nonparametric analyses were performed. The nonparametric analyses included the Kruskal-Wallis one-way analysis of variance followed by Dunn's Summed Rank Test if differences were indicated. Dose response was evaluated by Jonkheere's test of Ordered Response.
Results and discussion
Test results
- Sex:
- male/female
- 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: 500 - 2000 mg/kg bw
- Clinical signs of toxicity in test animals: No toxicity was observed up to the highest dose tested.
- Harvest times: 24 h
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei: Treatment of the animals with the test substance did not lead to a dose-dependent and statistically significant increase in micronuclei formation.
- Cytotoxicity: No cytotoxicity was observed, since there were no statistically significant decreases in the percentage of PCEs of the treated animals in comparison with the vehicle control.
Any other information on results incl. tables
Table 1: Results of the in-vivo micronucleus assay in male animals
|
%PCE at sampling time |
Total micronuclei per 1000 PCEs at sampling time |
||
Exp group |
Number of animals |
Dose [mg/kg] |
24 h |
24 h |
Vehicle control (peanut oil) |
5 |
0 |
54.14 ± 6.00 |
0.6 ± 0.7 |
Positive control (cyclophosphamide) |
5 |
20 |
40.24 ± 11.18** |
18.7 ± 7.5** |
Test substance |
5 |
500 |
54.76 ± 4.81 |
0.9 ± 0.4 |
Test substance |
5 |
1000 |
51.80 ± 7.46 |
1.2 ± 0.8 |
Test substance |
5 |
2000 |
51.84 ± 8.85 |
0.8 ± 0.6 |
**statistically significant (p<0.01)
Table 2: Results of the in-vivo micronucleus assay in female animals
|
%PCE at sampling time |
Total micronuclei per 1000 PCEs at sampling time |
||
Exp group |
Number of animals |
Dose [mg/kg] |
24 h |
24 h |
Vehicle control (peanut oil) |
5 |
0 |
55.30 ± 4.72 |
1.5 ± 0.4 |
Positive control (cyclophosphamide) |
5 |
20 |
44.54 ± 5.17** |
10.5 ± 3.4** |
Test substance |
5 |
500 |
56.26 ± 5.89 |
0.6 ± 0.4* |
Test substance |
5 |
1000 |
60.68 ± 3.63 |
0.8 ± 0.7* |
Test substance |
5 |
2000 |
59.90 ± 2.7 |
0.4 ± 0.4* |
*statistically significant (p<0.05);**statistically significant (p<0.01)
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results: negative
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