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EC number: 203-347-8 | CAS number: 105-95-3
- 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:
- no data
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study is non-GLP, it does not use the maximum tolerated dose or 2000 mg/kg bw, nor the minimum number of animals required by the OECD guideline No 474. However, 1600 and 1400 mg/kg bw are not so far from 2000 mg/kg bw, and 7 to 8 animals were used per dose level. Also, the intraperitoneal dose route was used, which is likely to achieve a greater exposure to the bone marrow than the oral route, which is the normal route currently used. Finally, a study done according to OECD standards is unlikely to provide a different result, particularly as there is no concern for genotoxicity in the other available in vitro studies.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- publication
- Title:
- Macrocyclic musk compounds - an absence of genotoxicity in the Ames test and the in vivo Micronucleus assay
- Author:
- Abramsson-Zetterberg L, Slanina P
- Year:
- 2 002
- Bibliographic source:
- Toxicology Letter 135: 155-163
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Deviations:
- yes
- Remarks:
- the maximum tolerated dose or 2000 mg/kg bw was not achieved, the minimum number of animals required was not used
- Principles of method if other than guideline:
- not applicable
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- 1,4-dioxacycloheptadecane-5,17-dione
- EC Number:
- 203-347-8
- EC Name:
- 1,4-dioxacycloheptadecane-5,17-dione
- Cas Number:
- 105-95-3
- Molecular formula:
- C15H26O4
- IUPAC Name:
- 1,4-dioxacycloheptadecane-5,17-dione
- Test material form:
- not specified
- Details on test material:
- - Name of test material: ethylene brassylate
- Analytical purity: 86 % (GC/MS)
- Source: Dr. G. Rimkus, Dept of Residue and Contamination Analysis, LVUA, Schleswig-Holstein, Neumünster, Germany
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- other: male CD-1 and female NMRI
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Uppsala
- Age at study initiation: 8-9 weeks
- Weight at study initiation: males: 30-40 g; females: 25-30 g
- Assigned to test groups randomly: yes, under following basis: - in Exp. 1 (males): 5 groups, 3 in each
- in Exp. 2 (females): 5 groups, 5 in each (except one with 4)
- Housing: no data
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS
no data
IN-LIFE DATES: no data
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- - Vehicle(s)/solvent(s) used: rape oil
- Dose volume: 10 mL/ kg bw - Details on exposure:
- none
- Duration of treatment / exposure:
- Exp. 1: 46 and 70 h; Exp. 2: 42 and 70 h
- Frequency of treatment:
- once
- Post exposure period:
- none
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
Exp. 1: 100, 1000 or 1600 mg/kg bw
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
Exp. 2: 350, 700 or 1400 mg/kg bw
Basis:
nominal conc.
- No. of animals per sex per dose:
- Exp. 1: 3 males per dose
Exp. 2: 5 females per dose, except the highest dose-group which includes only 4 females (1 died under anaesthesia) - Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Colchicine
- Justification for choice of positive control(s): direct acting agent with an aneugenic effect resulting in an increased fMPCE in peripheral blood at about 45 hours after treatment
- Route of administration: intraperitoneal
- Doses / concentrations: 1 mg/kg bw
Examinations
- Tissues and cell types examined:
- Polychromatic erythrocytes (PCE) from peripheral blood
- Details of tissue and slide preparation:
- TREATMENT AND SAMPLING TIMES (in addition to information in specific fields):
Blood samples were collected, under light anaesthesia with Fluothane, from the orbital plexus of each animal, at 46 and 70 h after injections in Exp. 1 and at 42 and 70 h after in,jections in Exp. 2. The choice of the first sampling time is based on the knowledge of the time between the appearance of polychromatic erythrocyte in bone marrow and peripheral blood. From each animal, about 50 µL blood was drawn at each sampling occasion. Two parallel aliquots of 5 µL blood were layered for purification on a 65 % Percoll gradient, as described by Grawé et al. (1993).
DETAILS OF SLIDE PREPARATION:
The cells in the pellet were fixed in a solution of glutaraldehyde according mainly to a method by Hayashi et al. (1992). The fixed cells were then stored during 1-2 days at 4 °C and the following staining was made in a buffer prepared by adding the fluorescent dyes Hoechst 33342 and thiazole orange to PBS. The samples from the two sampling occasions were stained and analysed at the same time.
METHOD OF ANALYSIS:
The samples were analysed on a dual laser FACStar Plus flow cytometer. The setting and equipment of the flow cytometer has been described before. From each of the peripheral blood samples about 100 000 PCE were analysed (from each animal at each occasion almost 200 000 PCE - two parallels - were analysed). - Evaluation criteria:
- a statistically significant difference between the treated and control groups should be demonstrated
- Statistics:
- Student t-test
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Remarks:
- only one female died under the anaesthesia
- Vehicle controls validity:
- valid
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay): no significant increase difference in the mean fMPCE (frequency of micronucleated PCE) in the groups of the animals treated as compared to the controls in both experiments.
- Ratio of PCE/NCE (for Micronucleus assay): see Table 7.6.2/1
- Appropriateness of dose levels and route:
- Statistical evaluation: no statistical difference between treated and control groups
- Positive control: In Exp. 1, the mice injected with colchicine showed a significant increase in the mean fMPCE at 46 h after the treatment. In Exp. 2, similarly treated mice showed a significant increase at 42 h.
Any other information on results incl. tables
Table 7.6.2: Results from the micronucleus test
Strain and sex |
N° of animals |
Treatment (mg/kg bw) |
Time after injection (h) |
PCE (%) |
PCE (No. of analysed) |
MPCE (No. Of scored) |
fMPCE (per mille) |
SD |
CD1, male |
3 |
Control |
46 |
2.7 |
594325 |
617 |
1.04 |
0.31 |
3 |
EB, 100 |
46 |
3.7 |
599023 |
648 |
1.08 |
0.15 |
|
3 |
EB, 1000 |
46 |
2.5 |
570505 |
524 |
0.92 |
0.22 |
|
3 |
EB, 1600 |
46 |
2.8 |
598598 |
592 |
0.99 |
0.13 |
|
3 |
Col, 10 |
46 |
0.7* |
211822 |
2172 |
10.25* |
0.17 |
|
3 |
Control |
70 |
2.9 |
564638 |
623 |
1.10 |
0.23 |
|
3 |
EB, 100 |
70 |
3.0 |
548490 |
666 |
1.21 |
0.16 |
|
3 |
EB, 1000 |
70 |
2.2 |
513417 |
473 |
0.92 |
0.26 |
|
3 |
EB, 1600 |
70 |
2.5 |
536533 |
535 |
1.00 |
0.10 |
|
3 |
Col, 10 |
70 |
1.0* |
293865 |
463 |
1.58 |
0.50 |
|
NMRI, female |
5 |
Control |
42 |
2.5 |
893089 |
1364 |
1.52 |
0.23 |
5 |
EB, 350 |
42 |
2.5 |
790404 |
1269 |
1.60 |
0.48 |
|
5 |
EB, 700 |
42 |
2.4 |
776752 |
1017 |
1.31 |
0.26 |
|
5 |
EB, 1400 |
42 |
2.7 |
903936 |
1271 |
1.40 |
0.19 |
|
3 |
Col, 10 |
42 |
1.7 |
375588 |
2334 |
6.18* |
4.4 |
|
5 |
Control |
70 |
2.7 |
753506 |
1304 |
1.73 |
0.21 |
|
5 |
EB, 350 |
70 |
1.9 |
665457 |
969 |
1.45 |
0.13 |
|
5 |
EB, 700 |
70 |
1.9 |
602829 |
806 |
1.34 |
0.22 |
|
4 |
EB, 1400 |
70 |
2.0 |
585127 |
855 |
1.46 |
0.39 |
|
4 |
Col, 10 |
70 |
1.9 |
405598 |
712 |
1.75 |
0.87 |
Col = Colchicine
* = Significant separated from the control
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
There was not a significant increase in the frequency of micronucleated polychromatic erythrocytes in bone marrow after any treatment time in both experiments. - Executive summary:
In an in vivo micronucleus assay conducted similarly to OECD 474 guideline, female NMRI and male CD-1 mice were intraperitoneally injected with Ethylene Brassylate diluted in rape oil. In experiment 1, males were dosed with 100, 1000 or 1600 mg/kg bw whereas in experiment 2, females were dosed with 350, 700 or 1400 mg/kg bw. Peripheral blood samples were collected at 46 and 70 h in experiment 1 and at 42 and 70 h in experiment 2.
All vehicle (solvent) controls had frequencies of micronucleated polychromatic erythrocytes (fMPCE) within the range expected for normal peripheral blood. The positive control material, Colchicine, induced statistically significant increases in the fMPCE at the first sampling time indicating the satisfactory performance of the test.
A female dosed with 1400 mg/kg bw died under anaesthesia. No other sign of toxicity was observed.
There was not a significant increase in the frequency of micronucleated polychromatic erythrocytes in bone marrow after any treatment time in both experiments.
Under the test conditions, the test material is not classified according to the annex VI of the Regulation EC No. 1272/2008 (CLP) and of the Directive 67/548/EEC.
The study is non-GLP, it did not use the maximum tolerated dose or 2000 mg/kg bw, nor the minimum number of animals required by the OECD guideline No. 474. However, 1600 and 1400 mg/kg bw are considered to be close to the maximum recommended dose level of 2000 mg/kg bw, and 7 to 8 animals were used per dose level, which is only 2 or 3 less than recommended. Also, the intraperitoneal dose route was used, which is likely to achieve a greater exposure to the bone marrow than the oral route, which is the standard route currently used. Finally, a study done according to the current OECD standard is unlikely to provide a different result, particularly as there is no concern for genotoxicity in the other available in vitro studies.
This study is therefore considered as acceptable and satisfies the requirement for in vivo cytogenetic mutagenicity data.
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