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EC number: 238-739-8 | CAS number: 14692-76-3
- 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:
- key study
- Study period:
- October/November 1994
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study without detailed documentation
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 994
- Report date:
- 1994
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 429 (Skin Sensitisation: Local Lymph Node Assay)
- GLP compliance:
- yes (incl. QA statement)
- Type of study:
- mouse local lymph node assay (LLNA)
Test material
- Reference substance name:
- Tetrasodium [3-[[8-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]-1-hydroxy-3,6-disulpho-2-naphthyl]azo]-4-hydroxynaphthalene-1,5-disulphonato(6-)]cuprate(4-)
- EC Number:
- 238-739-8
- EC Name:
- Tetrasodium [3-[[8-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]-1-hydroxy-3,6-disulpho-2-naphthyl]azo]-4-hydroxynaphthalene-1,5-disulphonato(6-)]cuprate(4-)
- Cas Number:
- 14692-76-3
- Molecular formula:
- C23H10ClCuN7Na4O14S4
- IUPAC Name:
- tetrasodium [3-[[8-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]-1-hydroxy-3,6-disulpho-2-naphthyl]azo]-4-hydroxynaphthalene-1,5-disulphonato(6-)]cuprate(4-)
- Reference substance name:
- tetralithium(1+) 5-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]-2λ³,25λ³-dioxa-13,14λ⁴-diaza-1-cuprahexacyclo[12.11.0.0³,¹².0⁴,⁹.0¹⁵,²⁴.0¹⁸,²³]pentacosa-3,5,7,9,11,13,15,17,19,21,23-undecaene-1,1-bis(ylium)-2,25-diide-7,11,17,22-tetrasulfonate
- Cas Number:
- 2112848-85-6
- Molecular formula:
- C23H10ClCuLi4N7O14S4
- IUPAC Name:
- tetralithium(1+) 5-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]-2λ³,25λ³-dioxa-13,14λ⁴-diaza-1-cuprahexacyclo[12.11.0.0³,¹².0⁴,⁹.0¹⁵,²⁴.0¹⁸,²³]pentacosa-3,5,7,9,11,13,15,17,19,21,23-undecaene-1,1-bis(ylium)-2,25-diide-7,11,17,22-tetrasulfonate
- Test material form:
- solid: particulate/powder
- Details on test material:
- Reactive Blue 13 Na/Li-Salt
Constituent 1
Constituent 2
In vivo test system
Test animals
- Species:
- mouse
- Strain:
- CBA
- Sex:
- male
- Details on test animals and environmental conditions:
- Specification: young adults
Husbandry: A maximum of 4 mice was housed per cage, in cages suitable for animals of this strain and weight range.
Diet: R&M No. 1, supplied by Special Diet Services Limited, UK and mains water, supplied by automatic system were available as libitum.
Water: tap water ad libitum
Acclimatization period: 5 days
Temperature: 21±2 °C
Relative humidity: 30-70%
Air: A minimum of 15 changes per hour
Light cycle: 12 h/ 12 h
Study design: in vivo (LLNA)
- Vehicle:
- propylene glycol
- Concentration:
- 3%, 10%, 30%
- No. of animals per dose:
- 4
- Details on study design:
- Approximately 25 µL of a 3, 10 and 30 % w/v preparation of the test substance in propylene glycol was applied, using a variable volume micro-pipette, to the dorsal surface of each ear. A vehicle control group was similarly treated using propylene glycol alone. The procedure was repeated daily for 3 consecutive days.
Three days after the third application, all the animals were injected, via the tail vein, with approximately 250 µL of phosphate buffer saline containing approximately 20 µCi of a 2.0 Ci/mmol specific activity 3H-methyl thymidine. Approximately 5 hours later, the animals were sacrificed by inhalation of halothane vapour followed by cervical dislocation. The draining auricular lymph nodes were removed from each animal and together with the nodes from the other animals in the group were placed in a container of PBS.
A single cell suspension was prepared by mechanical disaggregation of lymph nodes through a 200-mesh stainless steel gauze. The cell suspensions were then washed three times by centrifugation with approximately 10 mL of PBS. Approximately 3 mL of 5 % w/v trichloroacetic acid (TCA) was added and after overnight precipitation at 4 °C, the samples were pelleted by centrifugation and the supernatant was discarded. The cells were then resuspended in approximately 1 mL of TCA.
The lymph node suspensions were transferred to scintillation vials and 10 mL of scintillant was added prior to β-scintillation counting using a Packard Tri-Card 2500TH liquid Scintillation Counter.
Animals were checked at least once daily for signs of systemic toxicity. - Statistics:
- The results are expressed as a count per minute (cpm) value per lymph node for each group. The activity of each test group is then divided by the activity of the vehicle control group to give a test control ratio for each concentration.
The criterion for a positive response is that one or more concentrations of the test substance should elicit a 3-fold or greater increase in isotope incorporation relative to the vehicle control group.
Results and discussion
In vivo (LLNA)
Resultsopen allclose all
- Parameter:
- SI
- Value:
- 2.96
- Test group / Remarks:
- 3%
- Parameter:
- SI
- Value:
- 2.97
- Test group / Remarks:
- 10%
- Key result
- Parameter:
- SI
- Value:
- 3.07
- Test group / Remarks:
- 30%
- Cellular proliferation data / Observations:
- The EC3 for this substance was calculated to be 16%
Applicant's summary and conclusion
- Interpretation of results:
- Category 1B (indication of skin sensitising potential) based on GHS criteria
- Conclusions:
- The substance was shown to have the capacity to cause a very weak skin sensitization (SI=3.07) when applied as a 30% w/v preparation in propylene glycol.The EC3 for this substance was calculated to be 16%
- Executive summary:
A study was conducted to determine the skin sensitisation potential of the test substance in CBA/Ca mice according to OECD Guideline 406 (Local Lymph Node Assay), in compliance with GLP. The assay determined the level of T lymphocyte proliferation in the lymph nodes draining the site of chemical application by measuring the amount of radiolabelled thymidine incorporated into the dividing cells. Four male mice were used per test group. Approximately 25 µL of a 3, 10 and 30% w/v solution of test substance in propylene glycol was applied using a variable volume micro-pipette to the dorsal surface of each ear. Propylene glycol served as vehicle control. The procedure was repeated daily for 3 consecutive days. Animals were checked at least once daily for signs of systemic toxicity. Three days after the last application, all animals were injected with 3H-methyl thymidine and, after 5 hours the draining (auricular) lymph nodes were excised and pooled for each animal. After the samples preparation the lymph node suspensions were transferred to scintillation vials and 10 mL of scintillate was added prior to β-scintillation counting using a Packard Tri-Card 2500TH liquid scintillation counter. The substance was shown to have the capacity to cause a very weak skin sensitization when applied as a 30% w/v preparation in propylene glycol. The EC3 for this substance was calculated to be 16%
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