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EC number: 244-435-6 | CAS number: 21544-03-6
- 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 vitro
Administrative data
- Endpoint:
- in vitro gene mutation study in mammalian cells
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: GLP study performed according to a published procedure.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 985
- Report date:
- 1985
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- method according to Clive, D. et al Validation and characterization of the L5178Y/TK+/- mouse lymphoma mutagen assay system. Mutation Res. 59, 61-108 (1979)
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- mammalian cell gene mutation assay
Test material
- Reference substance name:
- Bis(2,3-epoxypropyl) cyclohexane-1,2-dicarboxylate
- EC Number:
- 226-826-3
- EC Name:
- Bis(2,3-epoxypropyl) cyclohexane-1,2-dicarboxylate
- Cas Number:
- 5493-45-8
- Molecular formula:
- C14H20O6
- IUPAC Name:
- bis(oxiran-2-ylmethyl) cyclohexane-1,2-dicarboxylate
- Test material form:
- liquid
Constituent 1
Method
- Target gene:
- Thymidine kinase genes
Species / strain
- Species / strain / cell type:
- mouse lymphoma L5178Y cells
- Details on mammalian cell type (if applicable):
- Mouse Lymphoma cells L5178Y, heterocygous subline, TK +/- (Obtained from Dr. D. Clive with burroughs wellcome Company Research TRiangle Park, N. C., USA).
- Additional strain / cell type characteristics:
- not specified
- Metabolic activation:
- with and without
- Metabolic activation system:
- S9 from Aroclor 1254 induced rats
- Test concentrations with justification for top dose:
- without metabolic activation: 1.2, 2.5, 5, 7.5, 10, 11.5 and 12.5 nl/ml (first experiment)
without metabolic activation: 2, 4, 8, 12, 16, 18 and 20 nl/ml (second experiment)
with metabolic activation: 10, 20, 40, 60, 80, 90 and 100 nl/ml (first experiment)
with metabolic activation: 8, 16, 32, 48, 64, 72 and 80 nl/ml (second and third experiment) - Vehicle / solvent:
- DMSO (1%)
Controls
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: Ethylmethane sulfonate (without S9 activation) and dimethylnitrosamine (with S9 activation)
- Details on test system and experimental conditions:
- The test substance was dissolved in DMSO, and diluted into the culture medium.
In a preliminary toxicity test the concentration of TGIC causing a 85% reduction of the viability of cells was determined in suspension growth after 4-hour treatment and 72 hour suspension growth of the cells.
For this test cells were taken from exponential growth phase in Fischer’s medium containing 10% horse serum and anti-biotics; the final concentration of DMSO in the cell culture medium was 1%.
Seven concentrations were tested (51.563 – 3300 nl/ml) in the first and second (0.7183 - 50 nl/ml) test.
Suspension growth was compared to control cultures of the same initial cell density. The concentration calculated to cause 85% reduction of relative growth was used as highest dose in the mutagenicity experiment.
The mutagenicity test was carried out using exponentially growing cells (free of TK -/- cells) at 3 x 10E5 cells/ml, in round bottom flasks. After cleaning of spontaneous mutants and an additional three-days incubation period in THG, the cells were treated for four hours with the selected concentrations.
S9-activating mix was prepared from livers of male rats treated with Aroclor 1254.
After the 4-hour treatment, cells were washed and resuspended in growth medium and grown for 72 hours. Cell counts were regularly adjusted to 3 x 10E5 cells/ml. At the end of this expression period, cells were transferred to culture tubes containing 5 ml semi-solid agar cloning medium: for each concentration 8 tubes were seeded with 4 x 10E5 cells, in cloning medium containing BudR at 50 ug/ml, for viability counts 4 tubes of each concentration were seeded with 200 cells each in cloning medium without BudR.
Incubation time was 14 to 16 days at 37°C, and 12 days for the viability tubes.
Colonies were counted with a Colony counter (Fisher Count-All, Model 600), and with the aid of the viability counts the relative number of mutant colonies (TK-/-) was determined.
The results are expressed as induced TK -/- mutants /10E6 surviving cells. Mutagenicity criteria is an increase of 2.5 above control in any of the concentrations tested.
Positive control were ethylmethanesulfonate for the experiment without, and dimethylnitrosamine for the experiment with S9-activation - Evaluation criteria:
- The results are expressed as induced TK -/- mutants /10E6 surviving cells. Mutagenicity criteria is an increase of 2.5 above control in any of the concentrations tested.
- Statistics:
- no data
Results and discussion
Test results
- Species / strain:
- mouse lymphoma L5178Y cells
- Metabolic activation:
- with and without
- Genotoxicity:
- positive
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
positive with and without metabolic activation
TK 12 608 caused mutagenic effects in the presence and absence of metabolic activation, and is therefore a direct-acting mutagen under the conditions of the assay. - Executive summary:
TK 12 608 was tested for mutagenic effects on histidine-auxotrophic mutants of Salmonella typhimurium. The investigations were performed on strains TA 98, TA 100, TA 1535 and TA 1537 with the following concentrations of the trial substance without and with microsomal activation: 20, 80, 320, 1280 and 5120 )ug/0.1 ml. In order to confirm the results, the experiments were repeated with the same concentrations.
These tests permit the detection of point mutations in bacteria induced by chemical substances. Any mutagenic effects of the substances are demonstrable on comparison of the numbers of bacteria in the treated and control cultures that have undergone backmutation to histidine-prototrophism. To ensure that mutagenic effects of metabolites of the test substances formed in mammals would also be detected, experiments were performed in which the cultures were additionally treated with an activation mixture(rat liver microsomes and co-factors).
In the experiments performed without microsomal activation treatment with TK 12 608 led to a marked increase in the number of back-mutant colonies of strains TA 100 and TA 1535. In the experiments carried out with microsomal activation this effect was more pronounced.
TK 12 608 and its metabolites formed as a result of microsomal activation thus displayed a clear-cut mutagenic effect in this test system.
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