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EC number: 428-480-0 | CAS number: 214559-61-2 COLORANT Y-1189; DUASYN; DYE Y-1189; FARBSTOFF Y-1189; Y-1189; Y-1189L
- 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

Endpoint summary
Administrative data
Link to relevant study record(s)
Description of key information
No quantitative data is available for oral, inhalation or dermal absorption. Given the physical chemical properties, absorption is expected to be practically zero via all routes. However in the absence of quantitative data ECHA defaults are assumed, not as a reflection of the actual absorption, but rather to reflect potential ratios of absorption between the routes that are important when making route to route extrapolations in deriving DNELs:
Oral absorption is taken as 50%, dermal absorbtion as 10% and dermal absorbtion as 50%.
For material that is absorbed, extensive metabolism and distribution is not expected. Excretion is likely to be mainly via the bile.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
- Absorption rate - oral (%):
- 50
- Absorption rate - dermal (%):
- 10
- Absorption rate - inhalation (%):
- 100
Additional information
Introduction
The physico-chemical properties and the results of repeat dose toxicity studies with animals for Y-1189 (CAS 214559-61-2, a sulphonated azo dye) have been used to estimate a toxicokinetic profile.
Physicochemical properties
The substance is an orange granular solid and has the molecular formula C26H24N6O13S6Na4 with a molecular weight of 912.85 g/mol. It is very water soluble (>1000 g/L at 20°C) with a log Pow value of < -4 at 20°C. It possesses sulphate groups, an azide bond and a triazine. It is not readily biodegradeable.
Absorption
No quantitative data is available for oral, inhalation or dermal absorption. Given the physical chemical properties, absorption is expected to be practically zero via all routes. However in the absence of quantitative data ECHA defaults are assumed, not as a reflection of the actual absorption, but rather to reflect potential ratios of absorption between the routes that are important when making route to route extrapolations in deriving DNELs.
Oral absorption
Given the very large molecular weight (approaching 1000) and the extremely low Kow, oral absorption is expected to be very low. This is supported by absence of adverse effects in the repeat dose toxicity studies, for which the NOAELs were set at the highest doses tested These NOAELs were 1000 mg/kg bw/day for parental, reproductive and developmental effects in the OECD 421 study (Petus – Árpásy, 2014; summarised at 7.8.1 and 7.8.2 (Dossier) / 5.9.1 (CSR)) and 600 mg/kg bw/day in an OECD 407 study (Lortie, 2002; Summarised at 7.5.1 (Dossier) / 5.6.1 (CSR)). In the absence of any quantitative information however 50% oral absorption is assumed.
Dermal absorption
No dermal absorption data is available for Y-1189. Given the very large molecular weight (approaching 1000) and the extremely low Kow, dermall absorption is expected to be practically zero. However in the absence of quantitative information and, on the basis of a molecular weight > 500 and a Kow >4, dermal absorption is taken as 10% (ECHA Guidance R.7)
Inhalation absorption
No data is available and inhalation absorption is assumed to be 100%
Distribution
No absorption is expected, but based on the high water solubility and low Kow, any material that was absorbed would not be expected to be distributed to fatty tissues. Highest concentrations might be expected in organs of excretion, particularly the liver where excretion of materials with a MW of >300 tends to happen via the bile. Given the low Kow and high water solubility no potential for bioaccumulation is anticipated.
Metabolism
No absorption is expected, but if some material were absorbed, because it is not readily biodegradeable, this might suggest that metabolism will not be extensive. Overall however, the potential for mammalian metabolism is not known.
Elimination
No absorption is expected, but materials with a MW of >300 tend to be excreted via the bile.
Conclusion
No quantitative data is available for oral, inhalation or dermal absorption. Given the physical chemical properties, absorption is expected to be practically zero via all routes. However in the absence of quantitative data ECHA defaults are assumed, not as a reflection of the actual absorption, but rather to reflect potential ratios of absorption between the routes that are important when making route to route extrapolations in deriving DNELs:
Oral absorbtion is taken as 100%, dermal absorbtion as 50% and dermal absorbtion as 10%.
For material that is absorbed, extensive metabolism and distribution is not expected. Excretion is likely to be via the bile.
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