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EC number: 211-463-5 | CAS number: 646-06-0
- 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
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- Solubility in organic solvents / fat solubility
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- Flash point
- Auto flammability
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- 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
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- 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
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- Nanomaterial catalytic activity
- Endpoint summary
- Stability
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- 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
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- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Genetic toxicity in vitro
Description of key information
A negative Ames test, a negative mouse lymphoma assay and a negative in vitro chromosome aberration test, one reliable negative cell transformation assay (CTA) and one non-reliable positive CTA.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Genetic toxicity in vivo
Description of key information
One reliable negative mouse bone marrow micronucleus test (MNT) and one non-reliable equivocal MNT, a negative dominant lethal test and a non-reliable DNA fragmentation assay.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (negative)
Additional information
1) In vitro genotoxicity:
1.1) Bacterial reverse gene mutation
Hargitai (2015), key study, reliability: 1
A fully guideline compliant bacterial reverse mutation assay (OECD471, GLP) was performed in the tester strains Salmonella typhimurium TA1535, TA1537, TA98, TA100 and Escherichia coli WP2, including analytical verification of the concentrations applied. In a plate incorporation assay and a pre-incubation assay there was no relevant increase in the number of revertants per plate in the absence and presence of metabolic activation up to the highest requested concentration of 5 mg/plate. Thus, this reliable and scientifically valid study demonstrated the non-mutagenicity of 1,3-dioxolane in bacterial test strains.
There is clear evidence that 1,3-dioxolane is not mutagenic.
1.2) Mammalian cell gene mutation
- Cifone (1985), key study, reliability: 1
The mutagenicity of 1,3-dioxolane was further evaluated in a GLP and OECD476 (version July 1997) compliant mouse lymphoma assay in three independent experiments. The cells were exposed to the substance up to the highest recommended concentration of 5 µL/mL without consideration of its volatility. Under the test conditions described, 1,3-dioxolane treatment did not result in an increased mutation frequency in the absence and presence of metabolic activation. This study with few methodological deficiencies is reliable, scientifically valid and appropriate for the assessment of 1,3-dioxolane as non-mutagenic in mammalian cells.
1.3) Chromosome aberration
- Ivett and Myhr (1985), supporting study, reliability: 3
A chromosomal aberration assay in Chinese hamster ovary cells provides supporting non genotoxic information on 1,3-dioxolane up to the limit dose of 5 mg/mL as requested by the OECD guideline 473 (volatility was not taken into account). There were major deviations to the guideline recommendations in this GLP study. In order to guarantee for a sufficient number of cells being in first post-treatment mitosis the cells should be harvested at a time point equivalent to 1.5 of the normal cell cycle time. In this chromosomal aberration study a cell harvest time of approximately 20 hours would have been adequate to fulfill this requirement. In the assay a shortened harvest time of 10 hours was applied, being less than a normal full cell cycle. The validity of the experimental parts were proven by the positive clastogenic response of the reference substances used. The outcome of this study was clearly that the test item was non-clastogenic under the conditions described, however, there was no independent repeat to confirm this result. This study with distinct methodological deficiencies is considered not to be sufficiently reliable to fully cover the endpoint structural (numerical) chromosome aberration, but considered to provide relevant supporting information to the results of the respective in vivo assays; and thus contributing to the weight of evidence for non-genotoxicity.
1.4) Genome mutation
Cell transformation assays are not limited to the detection of potential genotoxic agents, but can also identify substances acting as potential non-genotoxic carcinogens. There are currently no OECD guidelines in place for the tests briefly summarised below. Minor deviations, such as the lack of a metabolising system in the test and the lack of an experimental repeat for data confirmation, were noted as compared to the method described in Council Regulation (EC) 440/2008 B.21.
- Matthews and Myhr (1985), supporting study, reliability: 2
In a GLP compliant cell transformation assay, Balb/c 3T3 cells were treated with 1,3-dioxolane at 5 concentrations up to a maximum concentration of 15 µL/mL for a time period of 72 hours. The chosen concentrations covered the non-toxic, moderate toxic (approx. 78%) and clearly toxic (approx. 50%) range, and showed severe toxicity at the highest applied concentration. The complete concentration range was evaluated for morphological transformation and there was no increased incidence in the mean number of transformed foci up to the top concentration under the conditions of this study. This supporting study with methodological deficiencies is considered to be reliable with restriction and to provide relevant information contributing to the weight of evidence for non genotoxicity of 1,3-dioxolane.
- Garry and Kreiger (1981), disregarded study, reliability: 3
In a non-GLP compliant study a phase I colony mode test was performed, treating murine C3H10T1/2 cells with 0.1 µg/ml up to 10 mg/ml of 1,3-dioxolane in culture flasks and up to 20 mg/mL in culture dishes for 24 hours, followed by 14 days incubation before fixation and examination. In the phase II focus test cells were treated with 1 µg/ml up to 20 mg/ml in culture flasks and dishes for 24 h followed by 42 days incubation. The higher concentrations in flasks (2 – 20 mg/ml) showed contaminations, therefore information about transformation rates is lacking. In the phase I method, no transformed cells were observed using culture dishes. Thus, the single positive results in flasks (2 and 10 mg/ml), which were not dose-dependent, could not be confirmed. The phase II experimental part in culture flasks was discussed as being invalid due to the low response of the positive control. In contrast, in the phase II method a concentration-related increase in transformed foci was observed in dishes from 0.1 – 10 mg/mL, whereas at the highest applied concentration of 20 mg/mL, the number of transformed foci decreased; possibly linked to severe toxic effects. In the study report the outcome of the study is discussed as being positive due to the concentration-related increase in the phase II experiment in culture dishes. With regard to several deficiencies in study performance the positive findings should rather be discussed as being questionable. Most importantly, there are no cytotoxicity data for the phase II test, which are essential for evaluating the results, because a possible influence of test substance toxicity cannot be excluded. Additionally, there is no independent repeating experiment available, confirming the positive results. No criteria for the classification of a test substance as being positive were given in the report. In addition, there were no criteria defined for the acceptance of the reference substance showing a positive response. Finally, test substance concentrations of 5 – 20 mg/mL are far beyond the limit concentrations which are applied nowadays in the in vitro genetic toxicity assay systems. This non-GLP study with distinct methodological deficiencies is considered not to be reliable for the assessment of morphological cell transformation, and to provide a minor contribution to the weight of evidence.
2) In vivo genotoxicity:
2.1) Chromosome aberration
- Putman and Melhorn (1989), key study, reliability: 1
A GLP compliant mouse bone marrow micronucleus assay was performed in male and female animals at dose levels in a range of 525 to 2100 mg/kg bw with only minor deviations to the OECD guideline 474. The highest dose applied by intraperitoneal injections was slightly higher than the limit dose requested by the guideline. Cytotoxicity of 1,3-dioxolane was observed in the highest dose applied indicated as a reduction in the ratio of polychromatic to normochromatic erythrocytes (PCE/NCE), thus demonstrating bone marrow exposure. The evaluation of 1000 PCE at sampling times of 24, 48 and 72 hours revealed no treatment-related increases in the number of micronucleated cells. The current OECD guideline (latest revision Sept 2014) requests the evaluation of 4000 cells for micronucleus formation, however, since the criteria for a valid test were clearly fulfilled for the solvent and positive controls it was concluded that the outcome of the test was non-mutagenicity of 1,3-dioxolane. This key GLP study with few deviations to guideline is reliable and scientifically valid and demonstrates that 1,3-dioxolane is neither clastogenic nor aneugenic in vivo.
- Przybojewska et al. (1984), disregarded study, reliability: 3
In a mouse micronucleus study published by Przybojewska et al. (1984) male mice were treated twice (24 hours apart) with 1,3-dioxolane and bone marrow cells were prepared 6 hours after the last injection. The treatment resulted in a dose-related increase in PCE with micronuclei in a concentration range of 750 to 6000 mg/kg bw, showing statistical significance in a range of 1500 to 6000 mg/kg bw when compared to the concurrent vehicle control and thus the substance was considered to be mutagenic by the authors under the conditions of the test performance. This non-GLP study, however, is less reliable as compared to the key study since it did not follow the recommendations of the OECD guideline 474, resulting in distinct methodological deficiencies. The number of animals used for testing was below 5 mice per dose group, no data on toxicity (e.g. mortality, clinical signs, PCE/NCE ratio) were given for the main experiment and the sampling time should have been 18 - 24 hours after the last substance application. The lack of cytotoxicity data represents a major deficiency as positive results at highly toxic doses should be interpreted with caution. There are no data on the purity of the test substance batch used for the assay and thus it cannot be excluded that any impurity might be responsible for the observed effects. In addition, the two highest applied dose levels are far above the limit dose requested by the guideline. This non-GLP supporting study with clear methodological deficiencies and limited scientific validity provides equivocal evidence for the induction of chromosome aberrations by 1,3-dioxolane, which is overruled by the clearly negative result of the GLP and guideline compliant, reliable and scientifically valid key study by Putman and Melhorn (1989). The key study was conducted with a defined batch of high purity and its result is supported by the negative outcome of an in vitro chromosomal aberration assay by Ivett and Myhr (1985).
- Baranski et al. (1984), supporting study, reliability: 2
In a non-GLP dominant lethal study by Baranski et al. (1984) similar to OECD guideline 478 male rats were repeatedly dosed with 1,3-dioxolane by gavage (0.58 or 1.16 g/kg bw/d for 8 weeks) or exposed to the substance by whole body inhalation (2.5 mg/L, 5h/d for 12 months) and then mated with untreated females. All female animals were subject to examination of reproductive parameters. The male animals were examined for organ weight and histopathology of testicles. Minor deviations that were not considered to have affected the study were the missing data on substance batch and purity and the lack of a positive control. The lower number of animals was compensated with a longer evaluation period providing sufficient pregnant rats. Two dose levels were applied instead of three for oral exposure, however, toxic effects were observed at these levels and toxicity was also found for the concentration applied by inhalation. There was no evidence of a dominant lethal effect and the study is considered as being valid.
2.2) DNA damage / repair
- Jaros-Kaminska et al. (1985), disregarded study, reliability: 3
The interaction of 1,3-dioxolane with DNA in vivo (in hepatocytes, 4 hours after intraperitoneal injection in rats) was examined by Jaros-Kaminska et al. (1985) in an explorative non-GLP study. In hepatocyte DNA isolated from treated rats a statistical significant increase in single strand breaks was observed without showing any dose dependency. The calculated DNA fragmentation index was far below the values obtained for the reference substances. Interaction with DNA in vivo was observed, however, this is not an accepted method for the testing of genotoxicity. This non-GLP study conducted with a test item batch of unknown purity (purity not reported) is not considered to provide adequate information for a reliable assessment of the endpoint DNA fragmentation.
3) Overall conclusion:
There are sufficient data available from reliable and scientifically valid in vitro and in vivo studies to conclude that, based on the available weight of evidence,1,3-dioxolane does not exhibit a genotoxic potential. 1,3-Dioxolane was shown to be non-mutagenic in bacteria and mammalian cells. There was no indication for 1,3-dioxolane-related cell transformation based on key study results. 1,3-Dioxolane did not induce chromosome aberration according to the outcome of the key in vivo bone marrow micronucleus assay, as supported by the lack of clastogenic activity noted in an in vitro chromosome aberration assay. Supplementary in vivo data indicated that exposure to 1,3-dioxolane was not associated with a dominant lethal effect. The assessment of 1,3-dioxolane as being non-genotoxic both in vitro and in vivo is supported by the results of the 2-year carcinogenicity key study in rats (Busey, 1985) where no relevant increases in any tumor incidence of the animals were reported. In addition, no indication for a carcinogenic potential was found in the repeated dose oral and inhalation toxicity key studies performed by Hoberman (1991) and Landry et al. (1990).
Justification for selection of genetic toxicity endpoint
A variety of in vitro and in vivo genotoxicity assays consistently concluded that 1,3-dioxolane did not exhibit genotoxic potential.
Short description of key information:
- overall conclusion: non-genotoxic
- in vitro data: negative Ames test, a negative mouse lymphoma assay, a negative in vitro chromosome aberration test, one reliable negative cell transformation assay (CTA) and one non-reliable positive CTA
- in vivo data: one reliable negative mouse bone marrow micronucleus test (MNT) and one non-reliable equivocal MNT, a negative dominant lethal test and a non-reliable DNA fragmentation assay
Endpoint Conclusion: No adverse effect observed (negative)
Justification for classification or non-classification
Regarding the variety of in vitro and in vivo genotoxicity assays, it could be concluded that 1,3-dioxolane does not exhibit genotoxic potential. Therefore, a classification for mutagenicity according to Regulation (EC) No 1272/2008 is not warranted.
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