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EC number: 226-789-3 | CAS number: 5468-75-7
- 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)
- Endpoint:
- basic toxicokinetics, other
- Type of information:
- other: Expert statement
- Adequacy of study:
- key study
- Study period:
- 2020
- Reliability:
- 2 (reliable with restrictions)
- Details on absorption:
- A prerequisite for a relevant absorption is that the substance can be dissolved in either aque-ous (e.g., gastrointestinal fluid, blood plasma, sweat) or lipophilic (e.g., lipoproteins, lipid membranes, triglycerides) media or in both. C.I. Pigment Yellow 14 can be considered insol-uble because it has an extremely low solubility in water (0,8µg/L) and n-octanol (2,6 µg/L). Therefore, it is unlikely that C.I. Pigment Yellow 14 becomes systemically bioavailable after oral, dermal or inhalation exposure.
Based on the chronic oral toxicity study with C.I. Pigment Yellow 12 absorption of toxico-logically significant amounts via the gastrointestinal tract is considered unlikely, since C.I. Pigment Yellow 12 did not show any effects on inner organs and blood or urine. No metabo-lites were determined.
The skin sensitisation studies with the analogue substances C.I. Pigment Yellow 12 and C.I. Pigment Yellow 13 indicate no local dermal bioavailability. Systemic availability also seems to be negligible after dermal exposure since no systemic signs of intoxication were seen after occlusive administration of 500 mg C.I. Pigment Yellow 14 per kg body weight in rabbits in the acute dermal irritation study.
Dermal absorption is, therefore, considered unlikely.
In the unlikely event of exposure to aerosolized pigment in respirable form, the substance is considered to behave like an inert dust. Therefore, the deposited pigment particles will mostly be cleared from the lung via the mucocilliary transport. As the pigment will not dis-solve quickly in the lung surfactant, the only efficient way the pigment can enter the body is via phagocytosis of pigment particles by lung macrophages followed by migration of the macrophages into the interstitium and into the draining lymph nodes. However, the internal dose delivered via this mechanism can be considered negligible. - Details on distribution in tissues:
- The repeated dose toxicity study with the analogue substance C.I. Pigment Yellow 13 did not indicate any relevant histopathological changes in any of the investigated organs. In the sub-chronic inhalation study local effects were seen in the lungs, which were interpreted as the normal “clean-up” of the lung after inert dust exposure.
This may indicate that the pigment either does not affect specific organs as targets, i.e., is non-toxic, or is not distributed within the body in significant amounts. As indicated above, the physico-chemical parameters of the pigment support the conclusion that the pigment is not absorbed into the body and thus does not become systemically available. There were also no other signs of deposition of the pigment in any organ not exposed directly (except portal of entry: skin, lung, gut) including excretory organs, like the kidney, indicating that even exposure to high doses of the pigment does not lead to bioaccumulation in special compart-ments of the body.
Based on the available information on absorption distribution of the test material in the body in significant amounts is unlikely and specific hotspots of distribution cannot be identified.
Thus, it is concluded, that C.I. Pigment Yellow 14 is not systemically available at relevant concentrations within the organism.
There were no signs of bioaccumulation of the test material. The only exception could be the lung as portal of entry after prolonged exposure to excessive concentrations of dust (lung overload). This view is supported by the physical-chemical properties (solubility in water and octanol). - Details on excretion:
- Considering the physico-chemical properties and the molecular structure and size of the mol-ecules and the absence of any indication of absorption and/or metabolism it is assumed that excretion, if any, is likely to occur via faeces. This notion is confirmed by the discoloration of faeces observed in the oral studies as the only alteration.
- Metabolites identified:
- no
- Details on metabolites:
- Since the solution of the substance in cellular fluid or cellular membranes is a prerequisite for its metabolism, it is unlikely that the insoluble pigment becomes accessible for metabo-lizing systems in relevant amounts.
Diarylide yellow pigments are not or only to a negligible extend cleaved, taking into ac-count the negative results obtained with the analogue substances C.I. Pigment Yellow 12 and C.I. Pigment Yellow 13 in investigations on kinetic behavior.
The results of the mutagenicity tests provide qualitative information on the metabolic fate of C.I. Pigment Yellow 14. In the mutagenicity tests, the pigment proved to be non-mutagenic in the absence as well as in the presence of an exogenous metabolizing system, indicating that the pigment, even directly exposed to metabolizing enzymes, is not convert-ed into toxic or genotoxic metabolites. This conclusion is also supported by the lack of any morphological and histopathological changes of organs involved in xenobiotic metabolism, such as the liver, in the subacute to chronic toxicity studies with the analogue substances C.I. Pigment Yellow 12 and C.I. Pigment Yellow 13. Furthermore, the missing skin or eye irritating or skin sensitizing properties argue against any interaction with biological material.
Therefore, C.I. Pigment Yellow 14 is considered to just pass through the intestinal tract without significant metabolism. - Bioaccessibility (or Bioavailability) testing results:
- Bio-accessability is not likely
- Conclusions:
- Based on all available data, C.I. Pigment Yellow 14 does not exhibit conspicuous toxicoki-netic behaviour in the sense of accumulative and/or delayed effects with regard to the indi-vidual parameters absorption, distribution, metabolism and excretion. The only exception could be the lung as portal of entry after prolonged exposure to excessive concentrations of dust (lung overload).
The results from studies with dermal exposure indicate that C.I. Pigment Yellow 14 has a no relevant dermal absorptive potential. C.I. Pigment Yellow 14 is most probably not absorbed from the gastrointestinal tract in significant amounts.
Indications of an intense metabolism or a bio-accumulative potential do not exist as no tox-icity occurred even after chronic exposure, which points to no bio-accumulation potential and complete excretion of all possibly systemically available C.I. Pigment Yellow 13 and/or me-tabolites. - Executive summary:
Based on the available data base on C.I. Pigment Yellow 14 relevant information exists to make a qualitative evaluation of the toxicokinetic profile of this compound. This is in line with animal welfare considerations because additional animal tests can be avoided by such an evaluation. The substance is available in nano-form. The available data have partly been generated with non-specified material, but the conclusions drawn are considered valid for the nano form as well, because the material is chemically identical, and the physical properties are widely overlapping.
The results of basic toxicity testing give no reason to anticipate unusual characteristics regarding the toxico-kinetics of C.I. Pigment Yellow 14. C.I. Pigment Yellow 14 is not absorbed from the gastro-intestinal tract in toxicologically significant amounts. The data indicate that there is no relevant dermal absorption. After inhalation unspecific reactions to unreactive dust can be expected. Indications of a bio-accumulative potential as well as metabolism towards genotoxic sub-structures do not exist. Excretion of traces of possibly systemically available C.I. Pigment Yellow 14 and/or metabolites via faeces is likely.
Reference
Description of key information
Based on the available data base on C.I. Pigment Yellow 14 relevant information exists to make a qualitative evaluation of the toxicokinetic profile of this compound. This is in line with animal welfare considerations because additional animal tests can be avoided by such an evaluation. The substance is available in nano-form. The available data have partly been generated with non-specified material, but the conclusions drawn are considered valid for the nano form as well, because the material is chemically identical, and the physical properties are widely overlapping.
The results of basic toxicity testing give no reason to anticipate unusual characteristics regarding the toxico-kinetics of C.I. Pigment Yellow 14. C.I. Pigment Yellow 14 is not absorbed from the gastro-intestinal tract in toxicologically significant amounts. The data indicate that there is no relevant dermal absorption. After inhalation unspecific reactions to unreactive dust can be expected. Indications of a bio-accumulative potential as well as metabolism towards genotoxic sub-structures do not exist. Excretion of traces of possibly systemically available C.I. Pigment Yellow 14 and/or metabolites via faeces is likely.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
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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