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EC number: 203-473-3 | CAS number: 107-21-1
- 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 germ cell study: cytogenicity / chromosome aberration
- Remarks:
- Type of genotoxicity: chromosome aberration
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 986
Materials and methods
- Principles of method if other than guideline:
- Assessing the possible effects of ethylene glycol for reproduction and dominant lethal mutagenesis.
- GLP compliance:
- no
- Type of assay:
- rodent dominant lethal assay
Test material
- Reference substance name:
- Ethane-1,2-diol
- EC Number:
- 203-473-3
- EC Name:
- Ethane-1,2-diol
- Cas Number:
- 107-21-1
- Molecular formula:
- C2H6O2
- IUPAC Name:
- ethane-1,2-diol
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Further details see Reproduction Toxicity.
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- Further details see Reproduction Toxicity.
- Details on exposure:
- Further details see Reproduction Toxicity.
- Duration of treatment / exposure:
- Further details see Reproduction Toxicity.
- Frequency of treatment:
- daily
Doses / concentrationsopen allclose all
- Dose / conc.:
- 40 mg/kg bw/day (nominal)
- Dose / conc.:
- 200 mg/kg bw/day (nominal)
- Dose / conc.:
- 1 000 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 15
- Positive control(s):
- Further details see Reproduction Toxicity.
Examinations
- Tissues and cell types examined:
- Further details see Reproduction Toxicity.
- Details of tissue and slide preparation:
- Further details see Reproduction Toxicity.
- Statistics:
- Continuous data such as body weights were compared by analysis of variance validated by Bartlett's test for homogeneity of variance. Duncan's multiple range test wes used to identify individual mean differences when indicated by a significant F value. Where Bartlett's test indicated heterogeneous variances, t tests for equal or unequal variances were used to delineate differences between groups. Pup weights were compared by the method of Weil (Weil, 1970). Discontinuous data such as implantations and reproductive indices were compared by a multiple sum of ranks test. Frequency data were compared by the X2 test and by Fisher's exact test. The following reproductive indices were calculated and evaluated statistically by the previously described nonparametric methods: fertility index (male and female), days from first mating to parturition, gestation index (fraction of pregnancies that resulted in litters with live pups), gestation survival index (fraction of newborn pups alive at birth), 0 to 4-day survival index, 4 to 14-day survival index, 4 to 21day survival index. The last four indices are summarized in the tables as means for ease of understanding and presentation, although the nonparametric statistical methods did not include a comparison of means.
Results and discussion
Test results
- Key result
- Sex:
- male/female
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- valid
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Ethylene glycol administration did not lead to statistically significant adverse effects on any of the parameters measured in the three mating intervals. Slight apparent increases in the dominant lethal mutation index, observed during the week 2 mating for the high-dose (1.0 g/kg/day) group and during the week 3 mating for the low dose (0.04 g/kg/day) group, were probably random occurrences unrelated to EG treatment. This interpretation is consistent with the absence of a dose-response relationship and the fact that a negative index of similar magnitude (-8.2%) was observed for the low dose group in the week 2 mating. When compared to the combined control groups, significant decreases were observed as a result of TEM treatment for the number of females with implants, the total number of implants, and the number of live implants.
Any other information on results incl. tables
Summary of dominant lethal mutagenesis data:
Dose | Mating interval (week) | Females with implants | Total implants | Dead implants | Live implants | Dominant lethal mutations (%) | ||||
N | % | N | % | N | % | N | % | |||
1 g/kg/d | 1 | 13 | 87.7 | 128 | 9.8 | 6 | 0.46 | 122 | 9.4 | 0 |
2 | 13 | 86.7 | 107 | 8.2 | 10 | 0.77 | 97 | 7.5 | 11.0 | |
3 | 13 | 86.7 | 116 | 8.9 | 7 | 0.54 | 109 | 8.4 | -1.2 | |
0.2 g/kg/d | 1 | 11 | 73.3 | 108 | 9.8 | 10 | 0.91 | 98 | 8.9 | 5.3 |
2 | 14 | 93.3 | 132 | 9.4 | 14 | 1.00 | 118 | 8.4 | 1.2 | |
3 | 14 | 93.3 | 134 | 9.6 | 19 | 1.36 | 115 | 8.2 | 1.2 | |
0.04 g/kg/d | 1 | 11 | 73.3 | 107 | 9.7 | 8 | 0.73 | 99 | 9.0 | 4.2 |
2 | 13 | 86.7 | 131 | 10.1 | 11 | 0.85 | 120 | 9.2 | -8.2 | |
3 | 14 | 93.3 | 118 | 8.4 | 18 | 1.29 | 100 | 7.1 | 14.5 | |
0.0A | 1 | 13 | 86.7 | 116 | 8.9 | 10 | 0.77 | 106 | 8.1 | |
2 | 13 | 86.7 | 106 | 8.1 | 7 | 0.54 | 99 | 7.6 | ||
3 | 13 | 86.7 | 123 | 9.5 | 12 | 0.92 | 111 | 8.5 | ||
0.0B | 1 | 10 | 66.7 | 113 | 11.3 | 3 | 0.30 | 110 | 11.0 | |
2 | 11 | 73.3 | 109 | 9.9 | 5 | 0.45 | 104 | 9.4 | ||
3 | 11 | 73.3 | 100 | 9.1 | 11 | 1.00 | 89 | 8.1 | ||
TEM (0.5 mg/kg) | 1 | 3 | 20.0 | 7 | 2.3 | 3 | 1.00 | 4 | 0.75 | 92.0 |
2 | 8 | 53.3 | 15 | 1.9 | 4 | 0.50 | 11 | 1.37 | 83.9 | |
3 | 1 | 6.7 | 1 | 1.0 | 1 | 1.00 |
0 |
0.00. |
100.0 |
Applicant's summary and conclusion
- Conclusions:
- The absence of a genotoxic effect in the dominant lethal study is consistent with negative genotoxicity results from other studies with EG. Although mutagenic activity has been demonstrated in some studies the divergent results may be explained in part by the presence of impurities in the samples tested. Unpublished data from our laboratory indicate that small amounts of impurities such as oxidation products and storage contaminants such as iron compounds may substantially affect the results of in vitro mutagenicity assays of EG samples. Of course, different mutagenicity assays have distinct end points and varying sensitivities. Therefore, when several different tests are performed, contrasting results are not unexpected.
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