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EC number: 224-481-3 | CAS number: 4378-61-4
- 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
Description of key information
acute oral toxicity: The test item (C.I. Pigment Red 168) did not cause any mortality or clinical signs or necropsy findings after single oral gavage administration to male and female rats at 5000 mg/kg bw in a valid pre-guideline study. The LD50 (male/female rat) was greater than 5000 mg/kg body weight. In a similarly conducted study the test item did not cause any mortality, clinical signs or necropsy findings after single oral gavage administration to female rats at 15000 mg/kg bw. Acute dermal toxicity: Pigment Red 168 did not cause any mortality or clinical signs or necropsy findings after single dermal administration to male and female rats at 2000 mg/kg bw in a OECD guideline and GLP compliant study. Acute inhalation toxicity: Study was waived and classification for this endpoint is considered unwarranted. When aerosolized in respirable form, the substance is considered likely to behave like an inert dust.
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study with acceptable restrictions
- Remarks:
- Test performed prior to the implementation of the current acknowledged testing and GLP guidelines . The test conduct however was in principle very similar to the OECD TG 401 as adopted in 1981. Important aspects (e.g. 14 day-postobservation time) were considered.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 401 (Acute Oral Toxicity)
- Deviations:
- no
- GLP compliance:
- no
- Remarks:
- pre-guideline study
- Test type:
- standard acute method
- Limit test:
- yes
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: W. Gassner, Sulzfeld
- Weight at study initiation: male 130 to 160 g, female 105 to 110 g
- Fasting period before study: 16 hours
- Housing: conventional housing, 5 animals per cage
- Diet: Ssniff P 10 pellets, ad libitum
- Water. tap water, ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 +/- 1°C
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- oral: gavage
- Vehicle:
- not specified
- Details on oral exposure:
- VEHICLE
- Concentration in vehicle: 40 % suspension - Doses:
- 0 and 5000 mg/kg bw
- No. of animals per sex per dose:
- 5 males
5 females - Control animals:
- yes
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of weighing: weekly
- Necropsy of survivors performed: yes - Key result
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 5 000 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: no animals died within the 14 days observation period
- Mortality:
- - no deaths occurred
- Clinical signs:
- other: - post application faeces was stained red - ruffled coat
- Gross pathology:
- No macroscopic findings at scheduled necropsy.
- Interpretation of results:
- GHS criteria not met
- Remarks:
- Regulation (EC) 1272/2008
- Conclusions:
- Single application of 5000 mg test item per kg bw did not cause lethality in male and female rats during the 14 days observation period, resulting in a LD50 > 5000 mg/kg bw.
- Executive summary:
Male and female rats were subjected to test acute oral toxicity according to a protocol similar to OECD TG 401 (limit test). The test item was administered at one dose level of 5000 mg/kg bw to 5 male and 5 female rats. During the 14 days observation period no animals died and there were no ab normalities found in necropsy, thus leading to an LD50 > 5000 mg/kg bw.
Therefore, the test item has not to be classified for acute oral toxicity according to Regulation (EC) No 1272/2008.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- discriminating dose
- Value:
- 5 000 mg/kg bw
- Quality of whole database:
- reliable with restrictions
Acute toxicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Study conducted in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or no or minor methodological deficiencies, which do not affect the quality of the relevant results. The study report was conclusive, done to a valid guideline and the study was conducted under GLP conditions.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.3 (Acute Toxicity (Dermal))
- Deviations:
- no
- GLP compliance:
- yes
- Test type:
- standard acute method
- Limit test:
- yes
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Five male and five female Wistar (RccHan:WIST) strain rats were supplied by a reputable supplier. For full details please see full study report. On receipt the animals were randomly allocated to cages. The females were nulliparous and non pregnant. After an acclimatisation period of at least five days the animals were selected at random and given a number unique within the study by indelible ink-marking on the tail and a number written on a cage card. At the start of the study the animals weighed at least 200g, and were eight to twelve weeks of age. The weight variation did not exceed ±20% of the mean weight for each sex.
The animals were housed in suspended solid floor polypropylene cages furnished with woodflakes. The animals were housed individually during the 24 Hour exposure period and in groups of five, by sex, for the remainder of the study. Free access to mains drinking water and food (2014C Teklad Global Rodent diet supplied by Harlan Laboratories UK Ltd., Oxon, UK) was allowed throughout the study. The diet, drinking water and bedding were routinely analysed and were considered not to contain any contaminants that could reasonably be expected to affect the purpose or integrity of the study.
The temperature and relative humidity were set to achieve limits of 19 to 25°C and 30 to 70% respectively. Any occasional deviations from these targets were considered not to have affected the purpose or integrity of the study. The rate of air exchange was at least fifteen changes per hour and the lighting was controlled by a time switch to give twelve hours continuous light (06:00 to 18:00) and twelve hours darkness.
The animals were provided with environmental enrichment items which were considered not to contain any contaminant of a level that might have affected the purpose or integrity of the study. - Type of coverage:
- semiocclusive
- Vehicle:
- other: distilled water
- Details on dermal exposure:
- On the day before treatment the back and flanks of each animal were clipped free of hair.
Using available information on the toxicity of the test item, a group of five male and five female rats was treated with the test item at a dose level of 2000 mg/kg.
The appropriate amount of test item, moistened with distilled water, was applied as evenly as possible to an area of shorn skin (approximately 10% of the total body surface area). A piece of surgical gauze was placed over the treatment area and semi occluded with a piece of self adhesive bandage. - Duration of exposure:
- 24 hours
- Doses:
- 2000 mg/kg body weight
- No. of animals per sex per dose:
- 5
- Control animals:
- not required
- Details on study design:
- On the day before treatment the back and flanks of each animal were clipped free of hair.
Using available information on the toxicity of the test item, a group of five male and five female rats was treated with the test item at a dose level of 2000 mg/kg.
The appropriate amount of test item, moistened with distilled water, was applied as evenly as possible to an area of shorn skin (approximately 10% of the total body surface area). A piece of surgical gauze was placed over the treatment area and semi occluded with a piece of self adhesive bandage. The animals were caged individually for the 24 Hour exposure period. Shortly after dosing the dressings were examined to ensure that they were securely in place.
After the 24 Hour contact period the bandage was carefully removed and the treated skin and surrounding hair wiped with cotton wool moistened with distilled water to remove any residual test item. The animals were returned to group housing for the remainder of the study period.
The animals were observed for deaths or overt signs of toxicity ½, 1, 2 and 4 hours after dosing and subsequently once daily for fourteen days.
After removal of the dressings and subsequently once daily for fourteen days, the test sites were examined for evidence of primary irritation and scored according to the following scale from Draize J H (1977) "Dermal and Eye Toxicity Tests" In: Principles and Procedures for Evaluating the Toxicity of Household Substances, National Academy of Sciences, Washington DC p.31:
EVALUATION OF SKIN REACTIONS
Erythema and Eschar Formation Value
No erythema 0
Very slight erythema (barely perceptible) 1
Well-defined erythema 2
Moderate to severe erythema 3
Severe erythema (beef redness) to slight eschar formation (injuries in depth) 4
Oedema Formation
No oedema 0
Very slight oedema (barely perceptible) 1
Slight oedema (edges of area well-defined by definite raising) 2
Moderate oedema (raised approximately 1 millimetre) 3
Severe oedema (raised more than 1 millimetre and extending beyond the area of exposure) 4
Any other skin reactions, if present were also recorded.
Individual bodyweights were recorded prior to application of the test item on Day 0 and on Days 7 and 14.
At the end of the study the animals were killed by cervical dislocation. All animals were subjected to gross necropsy. This consisted of an external examination and opening of the abdominal and thoracic cavities. The appearance of any macroscopic abnormalities was recorded. No tissues were retained. - Statistics:
- No statistical analysis was performed.
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- > 2 000 mg/kg bw
- Based on:
- test mat.
- Mortality:
- There were no deaths.
- Clinical signs:
- other: There were no signs of systemic toxicity.
- Gross pathology:
- No abnormalities were noted at necropsy.
- Other findings:
- Red coloured staining was noted at the test sites of all animals during the study. The staining prevented accurate evaluation of erythema in all animals one and two days after dosing.
There were no signs of dermal irritation noted. - Interpretation of results:
- GHS criteria not met
- Remarks:
- Regulation (EC) 1272/2008
- Conclusions:
- The acute dermal median lethal dose (LD50) of the test item in the Wistar strain rat was found to be greater than 2000 mg/kg bodyweight.
- Executive summary:
Introduction. The study was performed to assess the acute dermal toxicity of the test item in the Wistar strain rat. The method was designed to be compatible with the following:
OECD Guidelines for the Testing of Chemicals No. 402 “Acute Dermal Toxicity” (adopted24 February 1987)
Method B3 Acute Toxicity (Dermal) of Commission Regulation (EC) No. 440/2008
Method.
A group of ten animals (five males and five females) was given a single, 24 hour, semi-occluded dermal application of the test item to intact skin at a dose level of 2000 mg/kg bodyweight. Clinical signs and bodyweight development were monitored during the study. All animals were subjected to gross necropsy.
Mortality.
There were no deaths.
Clinical Observations.
There were no signs of systemic toxicity.
Dermal Irritation.
No signs of dermal irritation were noted.
Bodyweight.
Animals showed expected gains in bodyweight over the study period except two male animals that showed bodyweight loss over the first week but expected gain in bodyweight over the second week.
Necropsy.
No abnormalities were noted at necropsy.
Conclusion.
The acute dermal median lethal dose (LD50) of the test item in the Wistar strain rat was found to be greater than 2000 mg/kg bodyweight.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- discriminating dose
- Value:
- 2 000 mg/kg bw
- Quality of whole database:
- reliable without restriction
Additional information
Justification for selection of acute toxicity – oral endpoint
In the posterior more profound key study acute toxicity was tested
in males and females.
Justification for selection of acute toxicity – dermal endpoint
only one study available
Justification for classification or non-classification
Due to the findings described above (LD50 oral in rats > 15000 mg/kg bw, LD50 oral in rats > 5000 mg/kg bw, LD50 dermal in rats > 2000 mg/kg bw) Pigment Red 168 has not to be classified as acute orally and dermally toxic according to the criteria laid down in Directive 67/548/EEC and in Regulation (EC) No 1272/2008.
It can reasonably be deduced that Pigment Red 168 does not exert systemic toxic effects after acute inhalation exposure and thus does not have to be classified according to the criteria laid down in Directive 67/548/EEC and in Regulation (EC) No 1272/2008, because
- Pigment Red 168 did not cause lethal effects after administration of a single oral dose of up to 15000 mg/kg bw in rats
- Pigment Red 168 did not cause lethal effects after administration of a single dermal dose up to 2000 mg/Kg bw in rats
- Pigment Red 168 does not have to be classified as skin irritating, and
- it is unlikely that Pigment Red 168 becomes systemically bioavailable after inhalation due to its extremely low solubility in water and n-octanol.
Therefore, it is concluded that Pigment Red 168, when aerosolized, is an inert dust and that testing is not necessary to reach the scientific conclusion that classification is not warrantable.
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