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The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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EC number: 946-517-3 | CAS number: -
- 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 irritation / corrosion
Administrative data
- Endpoint:
- skin corrosion: in vitro / ex vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 17 May 2016 to 09 June 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 017
- Report date:
- 2017
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 431 (In Vitro Skin Corrosion: Reconstructed Human Epidermis (RHE) Test Method)
- Deviations:
- yes
- Remarks:
- deviations not affecting integrity or validity of the study (see below)
- Qualifier:
- according to guideline
- Guideline:
- other: Method B.40bis (in Vitro Skin Corrosion Human Skin Model Test)
- Deviations:
- yes
- Remarks:
- deviations not affecting integrity or validity of the study (see below)
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Confidential
- IUPAC Name:
- Confidential
- Test material form:
- solid
- Details on test material:
- - Appearance/physical state: Brown solid
- Storage conditions: Room temperature in the dark
Constituent 1
In vitro test system
- Test system:
- human skin model
- Source species:
- human
- Cell type:
- non-transformed keratinocytes
- Cell source:
- foreskin from a single donor
- Source strain:
- other: neonatal
- Vehicle:
- unchanged (no vehicle)
- Control samples:
- yes, concurrent negative control
- yes, concurrent positive control
- Amount/concentration applied:
- Approximately 180 mg
- Duration of treatment / exposure:
- 3 minutes and 60 minutes
- Duration of post-treatment incubation (if applicable):
- 3 hours
- Number of replicates:
- Two
Results and discussion
In vitro
Resultsopen allclose all
- Irritation / corrosion parameter:
- % tissue viability
- Run / experiment:
- 3 minute exposure
- Value:
- 91.6
- Vehicle controls validity:
- not applicable
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Irritation / corrosion parameter:
- % tissue viability
- Run / experiment:
- 60 minute exposure
- Value:
- 99.4
- Vehicle controls validity:
- not applicable
- Negative controls validity:
- valid
- Positive controls validity:
- valid
- Other effects / acceptance of results:
- DIRECT MTT REDUCTION
- An assessment found the test item was able to directly reduce MTT. Therefore, an additional procedure using freeze-killed tissues was performed. However, the results obtained showed that negligible interference due to direct reduction of MTT occurred.
- It was therefore considered unnecessary to use the results of the freeze-killed tissues for quantitative correction of results or for reporting purposes.
ASSESSMENT OF COLOUR INTERFERENCE WITH THE MTT ENDPOINT
- The solution containing the test item was a beige colour.
- This was considered to not have the potential to cause colour interference with the MTT endpoint.
TEST ITEM, POSITIVE CONTROL ITEM AND NEGATIVE CONTROL ITEM
- Mean OD562 values and viabilities for the negative control, positive control and test item are given in Appendix 1 (attached).
- The relative mean viabilities for each treatment group are shown in the table below.
QUALITY CRITERIA
- The mean OD562 for the negative control treated tissues was 1.896 for the 3-Minute exposure period and 1.874 for the 60-Minute exposure period. The negative control acceptance criteria were therefore satisfied.
- The relative mean tissue viability for the positive control treated tissues was 3.0% relative to the negative control following the 60-minute exposure period. The positive control acceptance criterion was therefore satisfied.
- In the range 20 to 100% viability the Coefficient of Variation between the two tissue replicates of each treatment group did not exceed 30%. The acceptance criterion was therefore satisfied.
Any other information on results incl. tables
RELATIVE MEAN VIABILITIES FOR EACH TREATMENT GROUP
Exposure period |
Percentage viability negative control* |
Percentage viability positive control |
Percentage viability test item |
3 minute |
100 |
3.7 |
91.6 |
60 minutes |
100 |
3.0 |
99.4 |
* Mean viability of the negative control tissues is set at 100%
Applicant's summary and conclusion
- Interpretation of results:
- GHS criteria not met
- Conclusions:
- The relative mean viability of the test item treated tissues was 91.6% after 3 minutes exposure and 99.4% after 60 minutes exposure.
- Executive summary:
GUIDELINE
The study was performed in compliance with the OECD Guideline for the Testing of Chemicals No 431 In Vitro Skin Corrosion: Reconstructed Human EpiDermis (RHE) Test Method (28 July 2015) and Method B.40bis of Commission Regulation (EC) No 440/2008 of 30 May 2008, laying down test methods pursuant to Regulation (EC) No 1907/2006 of the European Parliament and of the Council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH). The purpose of the test was to evaluate the corrosivity potential of the test item using the EpiDerm Human Skin Model after treatment periods of 3 and 60 minutes. Corrosion is directly related to cytotoxicity in the EpiDerm tissue and is determined by reduction of MTT (3-[4,5-dimethylthiazol-2-yl]-2,5-diphenyltetrazolium bromide) to formazan by viable cells in the test item-treated tissues relative to the corresponding negative control. The results are used to make a prediction of the corrosivity potential of the test item.
METHODS
Duplicate tissues were treated with discs of the test item for exposure periods of 3 and 60 minutes. The test item was found to directly reduce MTT and therefore additional non-viable tissues were incorporated into the testing for correction purposes. Negative and positive control groups were treated for each exposure period. At the end of the exposure period the test item discs were removed from each tissue. At the end of the formazan extraction period each well was mixed thoroughly and triplicate 200 μL samples were transferred to the appropriate wells of a pre-labelled 96-well plate. The optical density (OD) was measured at 562 nm (OD562). Data are presented in the form of percentage viability (MTT reduction in the test item treated tissues relative to negative control tissues).
RESULTS
Mean viability of the negative control tissues was set at 100 % and quality criteria for acceptance of results were satisfied. Relative mean viabilities after 3 minutes exposure were determined to be 100 % (negative control), 3.7 % (positive control and 91.6 % (test item). Relative mean viabilities after 60 minutes exposure were determined to be 100 % (negative control), 3.0 % (positive control) and 99.4 % (test item).
CONCLUSION
The relative mean viability of the test item treated tissues was 91.6% after 3 minutes exposure and 99.4% after 60 minutes exposure.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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