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Reaction mass of tetrasodium 7,7'-(carbonyldiimino)bis[4-hydroxy-3-[(2-methyl-4-sulphonatophenyl)azo]naphthalene-2-sulphonate] and tetrasodium 4-[[1-hydroxy-6-[[[[5-hydroxy-6-[(2-methyl-4-sulphonatophenyl)azo]-7-sulphonato-2-naphthyl]amino]carbonyl]amino]-3-sulphonato-2-naphthyl]azo]benzoate and tetrasodium 4,4'-[carbonylbis[imino(1-hydroxy-3-sulphonatonaphthalene-6,2-diyl)azo]]dibenzoate
EC number: 942-930-8 | 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
Endpoint summary
Administrative data
Description of key information
The NOAEL was determined to be 1000 mg/kg bw/day.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- short-term repeated dose toxicity: oral
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- From January 15 to February 28, 1979
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: No GLP, aged study. Meets generally accepted scientific standards, well documented and acceptable for assessment.
- Qualifier:
- no guideline followed
- Deviations:
- not applicable
- Principles of method if other than guideline:
- 1000 mg/kg/day of FAT 11'110/N where administrated daily (5 times a week) by gavage over a period of 30 days to male and female rats.
- GLP compliance:
- no
- Limit test:
- yes
- Species:
- rat
- Strain:
- other: Tif: RAIf (SPF)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: approx. 4 weeks
- Weight at study initiation: males: 128 - 129 g, females: 113 - 115 g
- Housing: individual housing in Macrolon cages type 3 with standardized granulated soft wood bedding (Societé Parisienne des sciures Pantin)
- Diet (e.g. ad libitum): pelleted standard diet (Nafag No. 890) ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 ± 1
- Humidity (%): 55 ± 5
- Air changes (per hr): 15 - 17
- Photoperiod (hrs dark / hrs light): 14 / 10 - Route of administration:
- oral: gavage
- Vehicle:
- CMC (carboxymethyl cellulose)
- Remarks:
- 2%
- Details on oral exposure:
- DOSING SOLUTIONS:
daily prepared suspension of the test compound in CMC 2%; control animals received a similar trweatment with CMC 2% without the compound
VEHICLE
- Concentration in vehicle: 10% compound in CMC 2%
- Amount of vehicle (if gavage): 10 ml/kg - Duration of treatment / exposure:
- 4 weeks and 2 days of the 5th week (30 days)
- Frequency of treatment:
- 5 times a week (in total 22 doses)
- Remarks:
- Doses / Concentrations:
1000 mg/kg bw/d
Basis:
actual ingested - No. of animals per sex per dose:
- 20 (10 male and 10 female animals had to undergo a two week recovery period)
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Post-exposure recovery period in satellite groups: 2 weeks
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: mortality: daily (a.m. and p.m.), symptoms: daily
BODY WEIGHT: Yes
- Time schedule for examinations: weekly
FOOD CONSUMPTION:
- Time schedule: weekly
FOOD EFFICIENCY:
- Mean food conversion (g food/kg bw/day) was calculated according to the following formula: MFC = (weekly food consumption (g)) / (midweek body weight (g)) * 1000/7
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: by observation prior to dosing and after the treatment period
HEARING TEST: Yes
- Time schedule for examinations: prior to dosing and after the treatment period (by hand clapping)
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at test day 28
- Anaesthetic used for blood collection: No
- Animals fasted: Yes
- How many animals: 20 randomized rats (5 males, 5 females per group)
- Parameters examined: Hb, RBC, WBC (total count and differential count)
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: at test day 28
- Animals fasted: Yes
- How many animals: 20 randomized rats (5 males, 5 females per group)
- Parameters cexamined: GOT, GPT, AP
URINALYSIS: Yes
- Time schedule for collection of urine: at test day 28
- Animals fasted: Yes
- Parameters examined: pH, protein, glucose, urobilinogen, urine sediment - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
Macroscopical Examination: At the end of the 30 day toxicity study or after an additional recovery period of two weeks the treated and control rats were bled under ether anaesthesia and complete autopsy was carried out. The total weight of each animal was determined and following organs were weighed: liver, kidneys and adrenals. The mean organ weights and mean organ to body weight ratios of each of these organs were calculated for all treated and control groups.
HISTOPATHOLOGY: Yes
Tissue portions of trachea, lungs, liver, pancreas, salivary gland, stomach, small and large intestine, heart, spleen, lymph nodes, thymus, kidneys, urinary bladder, testicles or ovaries, prostate or uterus, pituitary, thyroid, adrenals, skeletal muscle, skin, malMlary glands, bone marrow, eyes, brain, spinal cord , sciatic nerve, oesophagus and all other organs and tissues which showed macroscopical changes were fixed in buffered 10 % formalin.
The fixed tissues samples of liver, kidneys and adrenals were embedded in paramat and cut at 3 - 5 µ. The routine stain was haematoxylin and eosin. Sections from liver, kidneys and adrenals were also stained by Perl's method for·iron.
Additional frozen sections from liver were specifically stained for fat with Sudan Ill. Only the liver, kidneys and adrenals were histologically examined. - Statistics:
- For each time point and parameter a uni-variate statistical analysis was conducted. Due to the routine manner of the analysis system parameter free methods were applied. The treated group was compared to the control group in respect of dispersion and displacement (Y. Lepage, Biometrika (1971) 58: pp. 213-217).
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- no effects observed
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Details on results:
- CLINICAL SIGNS AND MORTALITY
No animal died during the treatment and/or the recovery period. No clinical symptoms and no signs of local and/or systemic toxicity were observed.
BODY WEIGHT AND WEIGHT GAIN
The body weight gain of all treated and control rats was comparable during the test and the recovery period.
FOOD CONSUMPTION
The mean food consumption of all treated animals was comparable to the controls during the 30 days of administration and during the recovery period.
FOOD EFFICIENCY
The mean food conversion of the males and females of the treated group was comparable to the controls.
OPHTHALMOSCOPIC EXAMINATION
Eye examinition did not reveal any ocular changes.
AUDITORY PERCEPTION
No loss of hearing ability was registred.
HAEMATOLOGY
The observed haematological findings between treated rats and controls were unremarkable.
CLINICAL CHEMISTRY
In the assessment of blood chemistry values the findings were unremarkable and comparable to those of the controls.
URINALYSIS
The findings in the urine were unremarkable. Individual rats revealed some degree of physiological proteinuria including those of the control group. This is considered normal in laboratory rats.
ORGAN WEIGHTS
Organ weights and organ to bodyweight ratios revealed no statistically significant differences between treated and control animals.
GROSS PATHOLOGY
No compound related gross anatomical changes were noted.
HISTOPATHOLOGY
All minor changes seen in some control and treated rats were only incidental in nature and not related to the treatment withthe test item. - Dose descriptor:
- NOEL
- Effect level:
- > 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Critical effects observed:
- not specified
- Conclusions:
- It can be concluded from the observations made during the study that 1000 mg/kg/day of the test item produced no observable effects in male and female rats when administrated daily by gavage over a period of 30 days.
- Executive summary:
The toxicity of FAT 11'110/N was investigated during a period over 30 day on females and males rats by oral administration.
No observable effects were observed at a dosage of 1000 mg/kg/day.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 1 000 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- Two studies are available performed with the same structural analogue. Both were determined to be klimisch 2.
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Studies were performed with analogue substance 1 (please refer to IUCLID section 13).
Repeated dose toxicity: oral
The toxicity of the structural analogue was investigated in an oral repeated dose study. Ten Tif: RAIf (SPF) rats per sex were exposed to the test substance dissolved in a 2% carboymethyl cellulose solution via oral gavage. Animals received 1000 mg/kg bw/day, five times per week for a period of five weeks. Animals receiving the vehicle served as controls. Clinical signs, body weight, food intake, food efficiency, ophthalmoscopic examination, auditory perception, hematology, blood chemistry, urinalysis, gross pathology, organ weight and histopathology were investigated. No toxic effects were observed. Based on this information the NOEL was calculated to be 1000 mg/kg bw/day.
Leist et al (1982) published the results of subacute toxicity studies on eight selected colorants, including the structural analogue. These eight colorants were administered as 22 daily doses over a period of 30 days (no weekend dosing) at 1000 mg/kg body weight/day by gavage to 20 female and 20 male rats. Animals treated with the vehicle served as controls. In most cases the treatment period was followed by a 15-day recovery period. Clinical signs, body weight, food intake, hematology, blood chemistry, urinalysis, gross pathology, organ weight and histopathology were investigated. At this dose level all products were tolerated without irreversible signs of toxicity. The survey of data available indicated that the substances investigated exhibited a very low cumulative toxicity. The NOAEL for the structural analogue was therefore determined to be 1000 mg/kg bw/day.
Justification for selection of repeated dose toxicity via oral route - systemic effects endpoint:
There are two studies available. Both studies are performed with the same structural analogue. The study with the most detailed information has been selected as key.
Justification for classification or non-classification
No signs of toxicity were observed after repeated exposure to 1000 mg/kg bw in two studies with analogue substance 1. Based on this information classification for oral repeated dose toxicity is not warranted in accordance with EU Classification, Labeling and Packaging of Substances and Mixtures (CLP) Regulation No. 1272/2008.
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