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EC number: 201-188-9 | CAS number: 79-24-3
- 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:
- 1979
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: This study was conducted prior to GLP and test guidelines, but sufficient data is available for interpretation of results
Data source
Reference
- Reference Type:
- publication
- Title:
- Mutagenic evaluation of nitroparaffins in the Salmonella typhimurium/ mammalian-microsome test and the micronucleus test
- Author:
- Hite M and Skeggs H.
- Year:
- 1 979
- Bibliographic source:
- Environ Mutagen 1:383-389
Materials and methods
- Principles of method if other than guideline:
- Mice were orally administered doses of nitroethane as high as half of the LD50 value. In this test the incidence of micronuclei in polychromatic erythrocytes was examined. Used the method of Schmid W: Chemical mutagen testing on in vivo somatic mammalian cells. Agents Actions 3:77-85, 1973.
- GLP compliance:
- not specified
- Type of assay:
- micronucleus assay
Test material
- Reference substance name:
- Nitroethane
- EC Number:
- 201-188-9
- EC Name:
- Nitroethane
- Cas Number:
- 79-24-3
- Molecular formula:
- C2H5NO2
- IUPAC Name:
- nitroethane
- Details on test material:
- No additional information available.
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- The mice used to study nitroethane were of the Charles River (CD-1) strain. At the initiation of the study, the animals were about five weeks old. The males weighed 26.0-31.0 g and the females weighed 20.0-24.6 g. Mice were maintained in standard mouse boxes in an air-conditioned room (about 22C) with free access to food (Wayne Lab Blox) and water at all times.
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- No information.
- Details on exposure:
- Nitroethane was given orally in dosages of 0.25, 0.50 and 1.00 ml/kg/day. Dosages were selected on the basis of the highest tolerated doses in acute oral toxicity studies. In our laboratory, the 14-day oral LD50 in CD-1 mice was calculated to be 2.15 (1.74 - 2.66) ml/kg for nitroethane.
- Duration of treatment / exposure:
- See above.
- Frequency of treatment:
- Mice were given two daily doses of the appropriate compound.
- Post exposure period:
- Six hours after the last dose the animals were sacrificed by cervical dislocation.
Doses / concentrations
- Remarks:
- Doses / Concentrations:0.25, 0.50 and 1.00 ml/kg/dayBasis:other: oral gavage
- No. of animals per sex per dose:
- 14 male and 14 female controls8 males and 8 females/dose group
- Control animals:
- other: 1.0 ml/kg/day tap water orally
- Positive control(s):
- methylmethanesulfonate, 90 mg/kg/day, ip
Examinations
- Tissues and cell types examined:
- Bone marrow from both femora was harvested and prepared for microscopic analysis after the method of Schmid (1973). ReferenceSchmid, W. (1973). Chemical mutagen testing on in vivo somatic mammalian cells. Agents Actions 3:77-85
- Details of tissue and slide preparation:
- The marrow from each mouse was evacuated from the marrow canal into a siliconized centrifuge tube, using fetal calf serum, and the tubes were centrifuges for five minutes at 1000 rpm. The supernatant was removed with Pasteur pipettes, and the cells were then resuspended by mixing gently with siliconized pipettes in the small amount of serum remaining in the capillary part of the test tube. A drop of the cell suspension was placed on a clean glass microscope slide and spread in the conventional manner. Four slides were prepared for each mouse. The smears were air-dried on a slide dryer at 37C and dipped briefly into absolute methanol for fixation. The slides were stained with May-Grunwald Geimsa stain. The microscope slides were coded so that they could be read in a blind and random fashion. Approximately 3000 erythrocytes (polychromatic and normochromatic) from each mouse were examined for the presence of micronuclei.
- Evaluation criteria:
- No additional information available.
- Statistics:
- The results were statistically analyzed by an analysis of variance procedure using a rankit transformation of the data and Fisher's Least Significance Difference procedure for joint comparison between the negative control and a treated group (Harter (1960); Snedecor et al., (1967)).References:Harter, H.L. (1960). Expected values of normal order statistics. Biometrika 48:151-165Snedecor, G.W. and Cochran, W.G. (1967). Statistical Methods, 6th Ed. Ames, Iowa, Iowa State University Press, p 272.
Results and discussion
Test results
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- not examined
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Nitroethane did not cause a significant increase in the numbers of polychromatic erythrocytes with micronuclei when compared to corresponding negative control groups of mice. No evidence of a sex-related difference in the response to treatment was seen.The positive control agent, methyl methanesulfonate, gave the anticipated positive results in both studies.
Any other information on results incl. tables
Table 1 Micronucleus test in the mouse percent polychromatic erythrocytes with micronuclei.
Sex (number) | Nitroethane |
0 (tap water), 1.0 ml/kg/day, p.o. | |
Female (14) | 0.64 |
Male (14) | 0.53 |
Combined (28) | 0.58 |
0.25 ml/kg/day, p.o. | |
Female (8) | 0.44 |
Male (8) | 0.51 |
Combined (16) | 0.48 |
0.50 ml/kg/day, p.o. | |
Female (8) | 0.47 |
Male (8) | 0.67 |
Combined (16) | 0.57 |
1.0 ml/kg/day, p.o. | |
Female (8) | 0.57 |
Male (8) | 0.60 |
Combined (16) | 0.59 |
Positive Control - methyl methanesulfonate, 90 mg/kg/day, i.p. | |
Female (5) | 6.09* |
Male (5) | 5.76* |
Combined (10) | 5.92* |
*Significant at P<0.001
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): negativeNitroethane did not cause a significant increase in the numbers of polychromatic erythrocytes with micronuclei when compared to corresponding negative control groups of mice. No evidence of a sex-related difference in the response to treatment was seen.
- Executive summary:
The mutagenic potential of nitroethane was evaluated in the mouse micronucleus test. Nitroethane did not cause a significant increase in the numbers of polychromatic erythrocytes with micronuclei when compared to corresponding negative control groups of mice. No evidence of a sex-related difference in the response to treatment was seen.
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