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EC number: 270-096-9 | CAS number: 68411-04-1
- 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
Key value for chemical safety assessment
Effects on fertility
Description of key information
According to REACH Annex VIII Section 8.7.1 Column 2 a screening for reproductive/developmental toxicity (OECD 421 or 422) does not need to be conducted, if a prenatal developmental toxicity study (Annex IX, 8.7.2) is available. For Direct Blue 264 (CAS 68411-04-1) a GLP prenatal developmental toxicity study after repeated oral administration in Wistar rats with Direct Blue 264 (CAS 68411-04-1) according to TG OECD 414 is available. Therefore, the requirements of REACH Annex VIII Section 8.7.1 Column 2 are fulfilled and no screening for reproductive/developmental toxicity (OECD 421 or 422) must be conducted.
According to REACH Annex VIII Section 8.7.3 Column 1 an Extended One-Generation Reproductive toxicity study is required, if the available repeated dose toxicity studies indicate adverse effects on reproductive organs or tissues or reveal other concerns in relation with reproductive toxicity. In a ‘90-Day Repeated Dose Oral Toxicity Study in Wistar Rats with Direct Blue 264 including Fertility Parameters’ there were neither macroscopic lesions nor histological changes in this study that could be attributed to the treatment with the test item. The following male and female reproductive organs were histopathological examined: testes, prostate and seminal vesicles with coagulating glands as a whole, epididymides, ovaries, uterus with cervix and vagina. At histopathological evaluation, the testes were checked on completeness of cell populations, completeness of stages and degenerative changes. No treatment-related effects on the testicular histomorphology were observed. Further, no treatment-related effect on interstitial cell structure was noticed. Thus, the histopathological NOEL (no observed effect level) may be established at 1000 mg/kg bw (the highest dose tested). In an OECD Guideline 414 (Prenatal Developmental Toxicity Study) in Wistar pregnant female rats with Direct Blue 264 at dose levels of 250, 500, and 1000 mg/kg body weight per day administered on gestation days 5 to 19, no effects of Direct Blue 264 on pregnant females and foetuses were found at dose levels up to 1000 mg/kg body weight/day. The NOAEL (No Observed Adverse Effect Level) for both maternal toxicity and foetal toxicity of Direct Blue 264 in this study is considered to be 1000 mg/kg body weight/day (the highest dose tested). Therefore, an Extended One-Generation Reproductive toxicity study is not required based on REACH Annex IX Section 8.7.3 Column 1.
Effect on fertility: via oral route
- Endpoint conclusion:
- no study available
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Effects on developmental toxicity
Description of key information
In an OECD TG 414 study possible adverse effects on pregnant females and embryo-foetal development were assessed, which could arise from repeated exposure of Direct Blue 264 via oral administration (gavage) to female rats during gestation days 5 to 19. Nulliparous and non-pregnant females were mated with males (2:1 ratio) and divided into four groups based on their body weights on the day of sperm positive vaginal smears (GD 0). The 4 groups comprised 25 female Wistar rats in the control (C), the low dose (LD), the medium dose (MD) and the high dose (HD) groups. The following doses were evaluated: 0 (control), 250, 500 or 1000 mg/kg body weight/day.
All clinical signs observed in terminally sacrificed females were incidental or non- adverse in nature.
No treatment-related effect on body weight development, food consumption, prenatal data parameters, litter data parameters, thyroid weight and hormones, foetal anogenital distance and gross pathology of terminally sacrificed females was observed up to highest dose tested. Furthermore, no treatment-related and toxicologically relevant external, visceral or craniofacial findings were observed in the HD group.
No effects of Direct Blue 264 on pregnant females and foetuses were found at dose levels up to 1000 mg/kg body weight/day. The NOAEL (No Observed Adverse Effect Level) for both maternal toxicity and foetal toxicity of Direct Blue 264 in this study is considered to be 1000 mg/kg body weight/day (the highest dose tested).
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 1 000 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- GLP guideline study.
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Toxicity to reproduction: other studies
Additional information
No data.
Justification for classification or non-classification
In a ‘90-Day Repeated Dose Oral Toxicity Study in Wistar Rats with Direct Blue 264 including Fertility Parameters’ there were neither macroscopic lesions nor histological changes in this study that could be attributed to the treatment with the test item. The following male and female reproductive organs were histopathological examined: testes, prostate and seminal vesicles with coagulating glands as a whole, epididymides, ovaries, uterus with cervix and vagina. At histopathological evaluation, the testes were checked on completeness of cell populations, completeness of stages and degenerative changes. No treatment-related effects on the testicular histomorphology were observed. Further, no treatment-related effect on interstitial cell structure was noticed. Thus, the histopathological NOEL (no observed effect level) may be established at 1000 mg/kg bw (the highest dose tested). In an OECD Guideline 414 (Prenatal Developmental Toxicity Study) in Wistar pregnant female rats with Direct Blue 264 at dose levels of 250, 500, and 1000 mg/kg body weight per day administered on gestation days 5 to 19, no effects of Direct Blue 264 on pregnant females and foetuses were found at dose levels up to 1000 mg/kg body weight/day. The NOAEL (No Observed Adverse Effect Level) for both maternal toxicity and foetal toxicity of Direct Blue 264 in this study is considered to be 1000 mg/kg body
According to CLP classification criteria (Regulation (EC) No 1272/2008) a classification is not justified.
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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