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EC number: 826-122-1 | CAS number: 13431-57-7
- 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

Skin sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in chemico
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 2017-2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 442C (In Chemico Skin Sensitisation: Direct Peptide Reactivity Assay (DPRA))
- Version / remarks:
- adopted 04 February 2015
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- direct peptide reactivity assay (DPRA)
Test material
- Reference substance name:
- 3-(acetyloxy)-2,2-dimethylpropyl acetate
- EC Number:
- 826-122-1
- Cas Number:
- 13431-57-7
- Molecular formula:
- C9 H16 O4
- IUPAC Name:
- 3-(acetyloxy)-2,2-dimethylpropyl acetate
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- The test item was homogeneous by visual inspection.
Storage conditions: Room temperature
Batch No.: VFH-2016-08
In chemico test system
- Details on the study design:
- The test substance was prepared at a 100 mM concentration in acetonitrile considering a purity/contents of 99.0% and its molecular weight. The C-containing peptide was incubated with
the test substance in a ratio of 1:10 (0.5 mM peptide, 5 mM test substance) and the K-containing peptide in a ratio of 1:50 (0.5 mM peptide, 25 mM test substance).
Three samples of the test substance were incubated with each peptide. Additionally, triplicates of the concurrent vehicle control (= NC) were incubated with the peptides. The remaining non-depleted peptide concentration was determined thereafter by HPLC with gradient elution and UV-detection at 220 nm. In addition, calibration samples of known peptide concentration, prepared from the respective peptide stock solution used for test-substance incubation, were measured in parallel with the same analytical method.
The samples were prepared in suitable tubes, capped tightly and incubated at 25°C ± 2.5°C in the dark for 24 +/- 2 hours. Visual inspection for solubility was performed directly after sample preparation and prior to HPLC analysis. Unsolved samples were centrifuged or filtrated prior to injection into the HPLC in order to remove any unsolved particles. The HLPC analysis of the batch of samples started about 24 hours after sample preparation and the analysis time itself did not exceed 30 hours.
Negative control (NC): vehicle control = acetonitrile
Positive control (PC): Ethylene glycol dimethacrylate prepared as a 50 mM solution in acetonitrile.
Co-elution control: Sample prepared of the respective peptide buffer and the test substance but without peptide.
Results and discussion
- Positive control results:
- 67.6% (Cys-peptide) was depleted by the positive control substance ethylene glycol dimethacrylate using acetonitrile as solvent.
13.6% (Lys-peptide) was depleted by the positive control substance ethylene glycol dimethacrylate using acetonitrile as solvent.
In vitro / in chemico
Resultsopen allclose all
- Run / experiment:
- mean
- Parameter:
- other: Peptide depletion [%] Cys
- Value:
- 0.67
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
- Run / experiment:
- mean
- Parameter:
- other: Peptide depletion [%] Lys
- Value:
- 0.62
- Vehicle controls validity:
- valid
- Positive controls validity:
- valid
Applicant's summary and conclusion
- Interpretation of results:
- other: inactive in the direct peptide binding assay
- Executive summary:
The reactivity of the UVCB-substance towards synthetic cysteine (C)- or lysine (K)-containing peptides was evaluated in the Direct Peptide Reactivity Assay (DPRA). For this purpose, the
test substance was incubated with synthetic peptides for ca. 24 hours at ca. 25°C and the remaining non-depleted peptide concentrations were determined by high performance liquid chromatography (HPLC) with gradient elution and UV-detection at 220 nm.
The test substance was formulated at a 100 mM concentration in acetonitrile. Three samples of the test substance were incubated with each peptide in ratios of 1:10 (for C-containing peptide) or 1:50 (for K-containing peptide). Additionally, triplicates of the concurrent vehicle control (= VC) were incubated with the peptides. Additionally, triplicates of the concurrent vehicle control (= NC) were incubated with the peptides. Further, a co-elution control was performed in order to detect possible interference of the test substance with the peptides. The samples consisted of the test substance, vehicle and the respective peptide buffer but without peptide. Moreover, the samples were analyzed by measuring UV absorbance at 258 nm and the area ratio 220 nm / 258 nm was calculated as a measure of peak purity.
The mean C-peptide depletion, caused by the test substance was determined to be 0.67%.
The mean K-peptide depletion, caused by the test substance was determined to be 0.62%.
The mean peptide depletion was calculated to be 0.64% and therefore the substance was determined to be inactive in the direct peptide binding assay.
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