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EC number: 208-857-4 | CAS number: 544-01-4
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP compliant, guideline study, no restrictions, fully adequate for assessment.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 012
- Report date:
- 2012
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- GLP compliance:
- yes
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Diisopentyl ether
- EC Number:
- 208-857-4
- EC Name:
- Diisopentyl ether
- Cas Number:
- 544-01-4
- Molecular formula:
- C10H22O
- IUPAC Name:
- 3-methyl-1-(3-methylbutoxy)butane
- Details on test material:
- - Name of test material (as cited in study report): Diisopentyl ether
- Analytical purity: 99.2%
- Lot/batch No.: TAP 645
- Storage condition of test material: 2-8 °C
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- NMRI
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Sulzfeld, Germany
- Age at study initiation: 6 weeks old
- Weight at study initiation: 34.3 ± 2.2 g
- Housing: animals were group housed (5 animals per sex per cage) in labelled Macrolon cages (MIII type, height 15 cm)
- Diet (e.g. ad libitum): free access to pelleted rodent diet (SM R/M-Z from SSNIFF® Spezialdiäten GmbH, Soest, Germany)
- Water (e.g. ad libitum): free access to tap water.
- Acclimation period: at least 6 days.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 17.1-21.4°C
- Humidity (%): 40-70%
- Photoperiod (hrs dark / hrs light): 12h/12h
- Air changes (per hr): approx. 15 changes per hour
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- Corn oil
- Details on exposure:
- - Dose selection rationale: In order to set the dose levels for the main study, a dose range finding study was performed. One dose group of 3 females and 3 males received a single dose of 2000 mg/kg bw by oral gavage. The animals showed no treatment related clinical signs or mortality after dosing. Based on the results of this range finding study, dose levels for the main study were: 500, 1000 and 2000 mg/kg body weight. Since there were no differences between sexes in toxicity only male animals were used in the main study.
- Preparation of dosing solutions: The total dosages (500, 1000 and 2000 mg/kg bw) were adminstered as single dose by oral gavage. Feed was withheld 3-4 h prior to dosing. The dosing volume was 10 ml/kg body weight. Diisopentyl ether concentrations were prepared on the day of administration. - Duration of treatment / exposure:
- single dose
- Frequency of treatment:
- once
- Post exposure period:
- 24-48 hr
Doses / concentrations
- Remarks:
- Doses / Concentrations:
500, 1000, 2000 mg/kg bw
Basis:
nominal conc.
- No. of animals per sex per dose:
- 5 male animals
- Control animals:
- yes, concurrent vehicle
- Positive control(s):
- Cyclophosphamide (40 mg/kg bw) was administered once by oral gavage as a solution in physiological saline (dose volume 10 mL/kg bw).
Examinations
- Tissues and cell types examined:
- Bone marrow of the groups treated with diisopentyl ether was sampled 24 or 48 (highest dose only) hours after dosing. Bone marrow of the negative control group was isolated 24 hours after dosing and bone marrow of the positive control group was isolated 48 hours after dosing. Both femurs were removed and freed of blood and muscles. Both ends of the bone were shortened until a small opening to the marrow canal became visible. The bone was flushed with approximately 2 ml of fetal calf serum (Invitrogen Corporation, Breda, The Netherlands). The cell suspension was collected and centrifuged at 216 g for 5 min.
- Details of tissue and slide preparation:
- The supernatant was removed with a Pasteur pipette. A drop of serum was left on the pellet. The cells in the sediment were carefully mixed with the remaining serum. A drop of the cell suspension was placed on the end of a clean slide, which was previously immersed in a 1:1 mixture of 96% (v/v)
ethanol (Merck, Darmstadt, Germany)/ether (Merck) and cleaned with a tissue. The drop was spread by moving a clean slide with round-whetted sides at an angle of approximately 45° over the slide with the drop of bone marrow suspension. The preparations were air-dried, fixed for 5 min in 100% methanol (Merck) and air-dried overnight. Two slides were prepared per animal. The slides were automatically stained using the "Wright-stain-procedure" in an "Ames" HEMA-tek slide stainer (Miles, Bayer Nederland B.V.). - Evaluation criteria:
- The number of micronucleated polychromatic erythrocytes was counted in at least 2000 polychromatic erythrocytes. The ratio of polychromatic to normochromatic erythrocytes was determined by counting and differentiating at least the first 1000 erythrocytes at the same time. Micronuclei were only counted in polychromatic erythrocytes. Averages and standard deviations were calculated.
A micronucleus test is considered acceptable if it meets the following criteria:
a) The incidence of micronucleated polychromatic erythrocytes in the positive control animals should be above the historical control data range.
b) The positive control substance induced a statistically significant (Wilcoxon Rank Sum Test, one sided, p < 0.05) increase in the frequency of micronucleated polychromatic erythrocytes.
c) The incidence of micronucleated polychromatic erythrocytes in the control animals should reasonably be within the laboratory historical control data range - Statistics:
- A test substance is considered positive in the micronucleus test if:
- It induced a biologically as well as a statistically significant (Wilcoxon Rank Sum Test, one-sided, p < 0.05) increase in the frequency of micronucleated polychromatic erythrocytes (at any dose or at any sampling time) or and the number of micronucleated polychromatic erythrocytes in the animals are above the historical control data range.
A test substance is considered negative in the micronucleus test if:
- None of the tested concentrations or sampling times showed a statistically significant (Wilcoxon Rank Sum Test, one-sided, p < 0.05) increase in the incidence of micronucleated polychromatic erythrocytes and the number of micronucleated polychromatic erythrocytes in the animals are within the historical control data range.
Results and discussion
Test results
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Mortalities
The animals of the groups treated with 2000, 1000 and 500 mg diisopentyl ether/kg body weight and the animals of the negative and positive control groups showed no treatment related clinical signs of toxicity or mortality.
Micronucleus counts
- No increase in the mean frequency of micronucleated polychromatic erythrocytes was observed in the bone marrow of Diisopentyl ether treated animals compared to the vehicle treated animals.
- The incidence of micronucleated polychromatic erythrocytes in the bone marrow of all negative control animals were within the historical vehicle control data range.
- Cyclophosphamide induced a statistically significant increase in the number of micronucleated polychromatic erythrocytes
Normochromatic to polychromatic erythrocyte ratios
The groups that were treated with Diisopentyl ether showed no decrease in the ratio of polychromatic to normochromatic erythrocytes compared to the concurrent vehicle control group, indicating a lack of toxic effects of this test substance on erythropoiesis. The group that was treated with cyclophosphamide showed an expected decrease in the ratio of polychromatic to normochromatic erythrocytes compared to the vehicle control, demonstrating toxic effects on erythropoiesis.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negative
It is concluded that this test is valid and that diisopentyl ether is not clastogenic or aneugenic in the bone marrow micronucleus test when sampled at 24 and 48 hours post dosing of male mice up to a dose of 2000 mg/kg (the maximum recommended dose in accordance with current regulatory guidelines) under the experimental conditions described in this report. - Executive summary:
In a GLP-compliant erythrocyte micronucleus test, according OECD guideline 474, male animals were dosed via oral gavage with vehicle or with 2000, 1000 and 500 mg Diisopentyl ether per kg body weight. A positive control group was dosed via oral gavage with 40 mg cyclophosphamide (CP) per kg body weight. In total 6 treatment groups were used, each consisting of 5 animals. No treatment related clinical signs or mortality were noted in any animal.
Bone marrow of the groups treated with Diisopentyl ether was sampled 24 or 48 (highest dose only) hours after dosing. Bone marrow of the negative and positive control groups was harvested 24 and 48 hours after dosing, respectively. No increase in the mean frequency of micronucleated polychromatic erythrocytes was observed in the bone marrow of animals treated with Diisopentyl ether. The incidence of micronucleated polychromatic erythrocytes in the bone marrow of all negative control animals were within the historical vehicle control data range. Cyclophosphamide induced a statistically significant increase in the number of micronucleated polychromatic erythrocytes. Therfore, the study was considered valid.
The groups that were treated with diisopentyl ether showed no decrease in the ratio of polychromatic to normochromatic erythrocytes compared to the concurrent vehicle control group, indicating a lack of toxic effects of this test substance on erythropoiesis. The group that was treated with cyclophosphamide showed an expected decrease in the ratio of polychromatic to normochromatic erythrocytes compared to the vehicle control, demonstrating toxic effects on erythropoiesis.
It is therefore concluded that, under the conditions used in this study, Diisopentyl ether is not clastogenic or aneugenic in the bone marrow micronucleus test when sampled at 24 and 48 hours post dosing of male mice up to a dose of 2000 mg/kg (the maximum recommended dose in accordance with current regulatory guidelines).
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