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EC number: 947-403-6 | 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 sensitisation
Administrative data
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- secondary literature
- Justification for type of information:
- data is from safety assessment reports
Data source
Reference
- Reference Type:
- secondary source
- Title:
- Scientific Committee on Consumer Safety - SCCS
- Author:
- Scientific Committee on Consumer Safety -SCCS
- Year:
- 2 010
- Bibliographic source:
- Scientific Committee on Consumer Safety - SCCS, 2010
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- Principles of method if other than guideline:
- To assess the skin sensitization potential of the test chemical according to OECD 429 Guidelines
- GLP compliance:
- not specified
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- 3-[(4,5-dihydro-3-methyl-5-oxo-1-phenyl-1H-pyrazol-4-yl)azo]-N,N,N-trimethylanilinium chloride
- EC Number:
- 269-943-5
- EC Name:
- 3-[(4,5-dihydro-3-methyl-5-oxo-1-phenyl-1H-pyrazol-4-yl)azo]-N,N,N-trimethylanilinium chloride
- Cas Number:
- 68391-31-1
- Molecular formula:
- C19H22ClN5O
- IUPAC Name:
- N,N,N-trimethyl-3-[(3-methyl-5-oxo-1-phenyl-4,5-dihydro-1H-pyrazol-4-yl)diazenyl]anilinium chloride
- Test material form:
- solid
- Details on test material:
- Name of test material (as cited in study report):Basic Yellow 57Molecular formula:C19H22N5OClMolecular weight :371.5 (as chloride) Substance type:OrganicPhysical state:SolidPurity: 99.3% (HPLC)Lot/batch No.: 15
Constituent 1
In vivo test system
Test animals
- Species:
- other: Mice
- Strain:
- other: CBA/CaOlaHsd (nulliparous and non-pregnant)
- Sex:
- female
- Details on test animals and environmental conditions:
- No data
Study design: in vivo (non-LLNA)
Inductionopen allclose all
- Route:
- other: Topical application
- Vehicle:
- other: ethanol:water, 7:3 (v/v)
- Concentration / amount:
- 2.5%, 5% and 10% (w/v) solutions
Challenge
- Concentration / amount:
- 2.5%, 5% and 10% (w/v) solutions
- No. of animals per dose:
- Three dose groups of four female mice each, were chosen.
- Details on study design:
- RANGE FINDING TESTS:In a pre-study evaluation on 2 mice, 1%, 2.5%, 5% and 10% solutions were evaluated.The highest dose (10%) in the main study was considered by the study to be “the highest technically applicable concentration whilst avoiding systemic toxicity and excessive local irritation”. It cannot be excluded that Basic Yellow 57 is a skin sensitizer as the maximum test concentration (10%) is too low.MAIN STUDYA. INDUCTION EXPOSURENo. of exposures: 3Exposure period:3 daysTest groups: 3 test groups consisting of 4 female miceControl group: 1 received only vehicleSite: dorsal area of the ears Frequency of applications: dailyDuration: 3 days Concentrations: The applicationvolume, 25 μl was topically applied to the dorsal surface of ears of test group.OTHER: Five days after the firsttopical application, all mice were administered with radio-labelled thymidine (³HTdR) by intravenous injection via the tail vein.Approximately 5 hours after ³HTdR application all mice were killed. The draining lymph nodes were excised and pooled for each experimental group. After preparation of the lymph nodes, disaggregation and overnight precipitation of macromolecules, these precipitations were re-suspended and transferred to scintillation vials.The level of ³HTdR incorporation was then measured The level of ³HTdR incorporation was then measured by scintillation counting. The proliferative response of lymph node cells is expressed as the ratio of ³HTdR incorporation into lymph node cells of treated animals relative to that recorded in control mice (stimulation index). The proliferative capacity of pooled lymph node cells was determined by quantifying the incorporation of ³H-methyl thymidine
- Positive control substance(s):
- yes
- Remarks:
- α-hexylcinnamaldehyde was used as positive control, to show distinct increases in the stimulation index.
Results and discussion
- Positive control results:
- The positive control used affected an increase in stimulation index with an EC3 of 11.7%.
In vivo (LLNA)
Results
- Parameter:
- SI
- Value:
- 1.2
- Test group / Remarks:
- 2% Concentration
- Remarks on result:
- other: not sensitizing
- Cellular proliferation data / Observations:
- The Stimulation Index (S.I.) was below 3 in all dose groups. No dose response relation was noted.
Any other information on results incl. tables
Table 1: Stimulation Index of test and control groups
Concentration % | Test group | Stimulation Index |
2.5 | Basic Yellow 57 | 1.2 |
5 | Basic Yellow 57 | 1.5 |
10 | Basic Yellow 57 | 1.5 |
5 | Positive Control | 1.5 |
10 | Positive Control | 2.3 |
25 | Positive Control | 8.4 |
Applicant's summary and conclusion
- Interpretation of results:
- other: not sensitizing
- Conclusions:
- The Stimulation Index (S.I.) was below 3 in all dose groups. No dose response relation was noted. Calculation of the EC 3 value was not performed as the S.I. value did not reach or exceed 3 for any test concentration. The positive control used affected an increase in stimulation index with an EC3 of 11.7%.Based on the criteria of the test system, the test chemical was not a non-sensitizer when tested up to 10% in ethanol:water (7:3 v/v) in mice.
- Executive summary:
Mouse Lymph node assay [LLNA] was performed on groups of female mice to assess the skin sensitizing potential of the test chemical.The assay was performed according to OECD 429 Guidelines.
Three dose groups and a control group (receiving the vehicle only) of four female mice each, were chosen. Each test group of mice was treated by topical (epidermal) application to the dorsal surface of each ear lobe (left and right) with the different test item concentrations. The application volume, 25 μl, was spread over the entire dorsal surface of each ear lobe once daily for 3consecutive days. The control group was treated with the vehicle. Five days after the first topical application, all mice were administered with radio-labelled thymidine (³HTdR) by intravenous injection via the tail vein.
Approximately 5 hours after ³HTdR application all mice were killed. The draining lymph nodes were excised and pooled for each experimental group. After preparation of the lymph nodes, disaggregation and overnight precipitation of macromolecules, these precipitations were re-suspended and transferred to scintillation vials.
The level of ³HTdR incorporation was then measured by scintillation counting. The proliferative response of lymph node cells is expressed as the ratio of ³HTdR incorporation into lymph node cells of treated animals relative to that recorded in control mice (stimulation index).
α- hexylcinnamaldehyde was used as positive control, to show distinct increases in the stimulation index.
The Stimulation Index (S.I.) was below 3 in all dose groups. No dose response relation was noted. Calculation of the EC 3 value was not performed as the S.I. value did not reach or exceed 3 for any test concentration. The positive control used affected an increase in stimulation index with an EC3 of 11.7%.
Based on the criteria of the test system, the test chemical was not a non-sensitizer when tested up to 10% in ethanol:water (7:3 v/v) in mice.
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