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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
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: 942-803-7 | 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics, other
- Remarks:
- Assessment based on data set
- Type of information:
- calculation (if not (Q)SAR)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- accepted calculation method
- Justification for type of information:
- Assessment has been based on existing data set for the substance and through assessment of similar substances in this class.
Data source
Reference
- Reference Type:
- other company data
- Title:
- Unnamed
- Year:
- 2 020
- Report date:
- 2020
Materials and methods
- Objective of study:
- absorption
- distribution
- excretion
- metabolism
- toxicokinetics
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The approach taken is to consider the chemical structure and class of this substance and to look at the existing data set.
Literature checks were also made on the class of substance including other azo-dyes as well as considering the impact of lithium.
There were many references found in relation to both lithium ion in pharmaceutical uses and to other common sulphonated azo substances.
Searches for similar substances have been performed using commercial directories and the ECHA web-site to help provide a weight of evidence. - GLP compliance:
- not specified
Test material
- Reference substance name:
- Reaction products of 2,7-Naphthalenedisulfonic acid, 4-amino-6-[2-[5-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]-2-sulfophenyl]diazenyl]-3-[2-(2,5-disulfophenyl)diazenyl]-5-hydroxy-, pentasodium salt and lithium chloride
- EC Number:
- 942-709-6
- Molecular formula:
- Not applicable; this UVCB substance contains: C25H14ClN10O16S5.xLi.yNa, (x + y) = 5; 0 < (x,y) < 5 with 940.9 < MW < 1021.1 g/mol (UVCB substance), and traces of NaCl.
- IUPAC Name:
- Reaction products of 2,7-Naphthalenedisulfonic acid, 4-amino-6-[2-[5-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]-2-sulfophenyl]diazenyl]-3-[2-(2,5-disulfophenyl)diazenyl]-5-hydroxy-, pentasodium salt and lithium chloride
- Test material form:
- solid: particulate/powder
- Remarks:
- migrated information: powder
Constituent 1
- Radiolabelling:
- no
Results and discussion
Main ADME resultsopen allclose all
- Type:
- absorption
- Results:
- Evidence of at least some dermal absorption. No direct evidence or oral absorption.
- Type:
- distribution
- Results:
- Effect on colour of kidneys and excretion in urine suggests transportation
- Type:
- metabolism
- Results:
- No evidence of metabolic processes. No significant biodegradation suggesting biological stability.
- Type:
- excretion
- Results:
- Feacal excretion noted shortly after oral ingestion due to colour change. No reported urine discolouration after dosing.
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- There is evidence of absorption following dermal administration, but no evidence of direct organ toxicity.
A 28-day oral study in rats resulted in no clinical signs other than discolouration and all animals survived the maximum dose of 1000 mg/kg/day.
Animal testing performed for non-EU regulatory purposes resulted in a positive guinea pig maximisation test.
This class of substances are typically classified as sensitisers from in-vivo testing and it is considered that the substance under review will also absorb through the skin. Older testing done by non-maximised methods such as the Buehler method (ie topical application only) failed to give positive responses and this may be in part due to due to low levels of dermal penetration. However, results of testing by maximised methods (Magnusson and Kligman) where the substance is injected are more likely to have positive responses; these methods still rely on topical challenge so some dermal absorption is still necessary.
It is also noted that many older in-vivo assessments failed to see weak reactions due to local skin discolouration from dermal application of the dyes on tested animals. - Details on distribution in tissues:
- Minor changes were seen in some animals following repeated dosing, but these were very likely adaptive changes or non-treatment related background variations. The kidneys showed minor colour change and urine was discolored.
Transfer into organs
- Test no.:
- #1
- Observation:
- no transfer detectable
- Details on excretion:
- From oral testing, most material seems to pass through the GI tract and quickly excreted in feaces.
Metabolite characterisation studies
- Metabolites identified:
- no
- Details on metabolites:
- None found.
Evidence from biodegradation testing and effect or S-9 activation suggests little if any metabolic degradation.
Any other information on results incl. tables
|
|
Observations |
Acute oral tox |
> 2000 mg/kg |
No adverse effects. Some skin and mucous membrane discolouration, but may be from indirect contact with faeces. |
Acute dermal tox |
> 2000 mg/kg |
No adverse effects Skin discolouration noted, persisting for the duration of observations in some cases. Grooming may have led to oral exposure in some cases No direct evidence of absorption.
|
Skin irritation |
Not classified |
In-vivo testing performed for non-EU regulatory processes; no significant effects
|
Eye irritation |
Not classified |
In-vivo testing performed for non-EU regulatory processes; moderate eye irritation |
Skin sensitisation |
Positive |
In-vivo testing performed for non-EU regulatory processes; maximised Guinea pig study positive. Some dermal absorption is assumed.
|
In-vitro mutagenicity |
Negative |
Tests on bacterial and mammalian cells were conducted at up to the maximum recommended concentrations with no evidence of cyto-toxicity or mutagenic potential. The present of S-9 metabolic fraction had no impact on the findings; this does not mean that there is no metabolic process, but that any direct metabolites are similarly non-biologically active. |
Sub-acute toxicity |
NOAEL 100 mg/kg/day |
The NOAEL is based on maximum dose level of 1000 mg/kg/day. |
Biodegradation |
No significant biodegradation |
This endpoint can indicate aerobic metabolic processes by eukaryotic cells. The absence of apparent effects suggest that there could be a low rate of metabolism, and it is probably that excretion in urine is the main route of elimination. |
Applicant's summary and conclusion
- Conclusions:
The substance has low toxicity with no specific target organ identified. Lithium is known to have neurological effects at relatively high concentrations, but at levels far greater than any accidental ingestion of the substance.
• There is no evidence of oral absorption and from coloured faecal excretion, it is likely a significant proportio passes through the GI tract unchanged. Results from in-vivo skin sensitisation testing suggests dermal penetration can occur.
• Thre is no evidence that the substance, or any similar-coloured metabolite, is excreted in urine
• Evidence from biodegradation testing and effect or S-9 activation suggests little if any metabolic degradation.
• Lithium and sodium ions are readily absorbed by ingestion and will be distributed in blood; as part of the natural ionic balance, excess sodium and lithium are excreted.
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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