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EC number: 945-065-4 | 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
Repeated dose toxicity: oral
Administrative data
- Endpoint:
- repeated dose toxicity: oral
- Remarks:
- combined repeated dose and carcinogenicity
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Justification for type of information:
- Data is from peer reviewed publication
Data source
Reference
- Reference Type:
- publication
- Title:
- Repeated dose oral toxicity study of the test chemical
- Author:
- Borzelleca et al
- Year:
- 1 989
- Bibliographic source:
- Fd Chem. Toxic
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: Refer below principle
- Principles of method if other than guideline:
- Toxicity of the test chemical was assessed in Sprague Dawley rats in life time study
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- Disodium 6-hydroxy-5-[(2-methoxy-4-sulphonato-m-tolyl)azo]naphthalene-2-sulphonate
- EC Number:
- 247-368-0
- EC Name:
- Disodium 6-hydroxy-5-[(2-methoxy-4-sulphonato-m-tolyl)azo]naphthalene-2-sulphonate
- Cas Number:
- 25956-17-6
- Molecular formula:
- C18H16N2O8S2.2Na
- IUPAC Name:
- disodium 6-hydroxy-5-[(2-methoxy-3-methyl-4-sulfonatophenyl)diazenyl]naphthalene-2-sulfonate
- Details on test material:
- - Name of test material: FD & C RED NO. 40 (ALLURA RED)
- IUPAC name: disodium 6-hydroxy-5-[(2-methoxy-4-sulphonato-m-tolyl)azo]naphthalene-2-sulphonate
- Substance type: Organic
- Physical state: solid
- Purity: 88%
- Impurity: 12%
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on species / strain selection:
- No data
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories. Inc., Wilmington, MA
- Age at study initiation: 90 days old approx.
- Weight at study initiation: no data
- Fasting period before study: no data
- Housing: rats were housed individually in stainless-steel cages except during the mating, lactation and post-weaning periods of the in utero phase
- Diet (e.g. ad libitum): Control animals received Purina Laboratory Chow and the treated animals received the appropriate dietary admixture
- Water (e.g. ad libitum): No data
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-21°C
- Humidity (%): 40-60%
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12-hr light/dark cycle
IN-LIFE DATES: From: To: No data
Administration / exposure
- Route of administration:
- oral: feed
- Details on route of administration:
- No data
- Vehicle:
- other: Purina Laboratory Chow
- Details on oral exposure:
- PREPARATION OF DOSING SOLUTIONS: The test material was incorporated into the basal diet using a Patterson-Kelley twin shell blender and used at dose levels of 0.0, 0.37, 1.39 and 5.19% (0, 180, 701, 2829 mg/kg bw/day males and 0, 228, 901, 3604 mg/kg bw/day for females)
DIET PREPARATION
- Rate of preparation of diet (frequency): Fresh diets were prepared and presented weekly.
- Mixing appropriate amounts with (Type of food): Purina
Laboratory Chow
- Storage temperature of food: No data
VEHICLE
- Justification for use and choice of vehicle (if other than water): Purina Laboratory Chow
- Concentration in vehicle: 0.0, 0.37, 1.39 and 5.19% (0, 180, 701, 2829 mg/kg bw/day males and 0, 228, 901, 3604 mg/kg bw/day for females)
- Amount of vehicle (if gavage): No data
- Lot/batch no. (if required): No data
- Purity: No data - Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- No data
- Duration of treatment / exposure:
- Males: 118 weeks
Females: 121 weeks - Frequency of treatment:
- 1 wk before mating, throughout the 3-wk breeding period, and during the gestation and lactation periods
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
Males: 0.0, 0.37, 1.39 and 5.19% (0, 180, 701, 2829 mg/kg bw/day)
Basis:
nominal in diet
- Remarks:
- Doses / Concentrations:
Females: 0.0, 0.37, 1.39 and 5.19% (0, 228, 901, 3604 mg/kg bw/day)
Basis:
nominal in diet
- No. of animals per sex per dose:
- 30/sex/group
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- The dietary concentrations for this study were selected based on the results of previous subchronic studies in rats
- Positive control:
- No data
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: gross signs of toxicity, death and morbidity were recorded daily. The rats were observed twice daily (5 days/wk) during the last 6 months of the study to minimize the loss of tissue to autolysis in rats that died on test.
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: weekly for wk 0 10, bi-weekly for wk 12-26, and every 4 wk thereafter
BODY WEIGHT: Yes
- Time schedule for examinations: weekly for wk 0 10, bi-weekly for wk 12 26, and every 4 wk thereafter
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):Yes weekly for wk 0 10, bi-weekly for wk 12 26, and every 4 wk thereafter
FOOD EFFICIENCY: No data
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): No data
OPHTHALMOSCOPIC EXAMINATION: No data
HAEMATOLOGY: Yes
- Time schedule for collection of blood: Blood samples were obtained from the tail vein during the study, and from the abdominal aorta at termination test were conducted at wk 13, 26, 52 and 78 and at termination
- Anaesthetic used for blood collection: No data
- Animals fasted: No data
- How many animals: five rats/sex/group
- Parameters checked : haematocrit, haemoglobin, erythrocyte count, and total and differential leucocyte counts.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: Blood samples were obtained from the tail vein during the study, and from the abdominal aorta at termination and clinical chemistry studies were performed on at week 52 and at termination
- Animals fasted: No data
- How many animals: 5 rats/sex/group
- Parameters checked: aspartate aminotransferase, Alanine aminotransferase, alkaline phosphatase, blood urea nitrogen, fasting glucose, total protein, sodium, potassium, chloride, carbon dioxide (termination only) and serum electrophoresis
URINALYSIS: Yes
- Time schedule for collection of urine: Urine samples were obtained by housing rats overnight in individual metabolism cages. Urinary analysis was conducted at wk 13, 26, 52, 78 and at termination
- Metabolism cages used for collection of urine: Yes
- Animals fasted: No data
- Parameters checked : specific gravity, pH, glucose, ketones, total protein, bilirubin and sediment.
NEUROBEHAVIOURAL EXAMINATION: No data
OTHER: - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
Gross autopsies were conducted on all rats that died spontaneously, were killed in a moribund condition, or were killed at the end of the study. Rats were killed by exsanguination under sodium pentobarbital. Absolute and relative organ weights were determined for the heart, liver, spleen, kidneys, testes with epididymides, and thyroid and adrenal glands.
HISTOPATHOLOGY: Yes
Complete histology was conducted on all rats from the control and high-dose groups. The following tissues from these rats were examined histologically: brain, pituitary, thoracic spinal cord, eyes, oesophagus, thyroid, thymus, heart, lungs, liver, spleen, pancreas, stomach, small and large intestine, mesenteric lymph node, kidneys, adrenal, urinary bladder, uterus, prostate, ovaries, testes with epididymides, seminal vesicles, skin, rib junction, bone marrow, nerve with muscle, and any tissue masses or lesions. Histology was also conducted on animals from any group with grossly observed masses or lesions. If a potential effect was consistently noted in a tissue then that tissue was examined histologically in all rats. All excised tissues not exhausted for histology were preserved. - Statistics:
- Gain in group mean body weight and total food consumption for weeks 0-54, group mean body weight at termination, and absolute and relative organ weights were analysed by the methods of Bartlett (1937), Snedecor and Cochran (1967) and Scheffe (1953). Survival data were analysed by the methods of Sachs (1959) and Snedecor and Cochran (1967). Tumour incidence data were analysed by the methods described by Thomas et al. (1977). All analyses were considered
significant at P <0.05. Time-to-tumour analyses were not performed because data correlating the time of tumour development to the time of death were not
generated.
Results and discussion
Results of examinations
- 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:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- not specified
- Immunological findings:
- not specified
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- not specified
- Details on results:
- CLINICAL SIGNS AND MORTALITY
There were no compound-related effects on survival
Localized hair loss (apparently due to friction against the cage) and nasal and ocular discharge occurred at low incidences throughout the study in control and treated rats. A red tint to the fur was noted in treated rats, and the faeces of mid- and high-dose rats were red. Palpable masses were noted with equal incidences in the control and treated groups.
Survival at the end of the study was similar in control and treated groups
BODY WEIGHT AND WEIGHT GAIN
Group mean body weights at the end of the study were decreased in rats that received FD & C Red No. 40 except for the mid-dose 701 mg/Kg bw/day males, in which they were increased.The mean body weight of the high-dose 3604 mg/Kg bw/day females at the end of the study was significantly less than that of the controls.
FOOD CONSUMPTION
Food consumption were increased in 2829 mg/Kg bw/day foe males and 3604 mg/Kg bw/day for females in the treated group but not significantly so as compared to control
HAEMATOLOGY
Few of the hematological differed significantly between control and treated rats, and none of the differences were compound related.
CLINICAL CHEMISTRY
Few of the Clinical chemistry differed significantly between control and treated rats, and none of the differences were compound related.
URINALYSIS
Few of the urinanalysis differed significantly between control and treated rats, and none of the differences were compound related.
ORGAN WEIGHTS
No compound-related changes in organ weights, were noted in rats that died on test or that were killed in a moribund state or at the end of the study.
GROSS PATHOLOGY
No compound related adverse effect observed
HISTOPATHOLOGY:
Histological evaluation revealed a variety of lesions, including neoplasm, among the control and treated rats.
The lesions were present at similar incidences in control and treated rats and appeared to be spontaneous. None of the lesions were determined to be related to the administration of FD & C Red No. 40.
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 2 829 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- other: No compound-related adverse effects were observed
- Dose descriptor:
- NOAEL
- Effect level:
- 901 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- body weight and weight gain
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Table 1. Mean food and compound consumptions of rats in the diet in utero and throughout their lifetimes
Dietary concn (%) |
Food consumption (g/kg/day) |
Compound consumption (mg/kg/day) |
||
Males |
Females |
Males |
Females |
|
0.0 |
49.2 |
60.7 |
- |
- |
0.37 |
48.8 |
63.4 |
180 |
228 |
1.39 |
50.3 |
63.5 |
701 |
901 |
5.19 |
54.6 |
69.1 |
2829 |
3604 |
Table 2. Survival and group mean body weights of rats {F1} given the test chemical in the diet in utero and throughoul their lifetimes
Dietary concn of (%) |
No. surviving at the end of the study ÷ |
Body weight (g) : |
|
Mean±SD |
Difference from control value |
||
Males |
|||
0.0 |
14 |
466 ±2 9 |
- |
0.37 |
12 |
454 ± 79 |
-2.6 |
1.39 |
14 |
503 ± 81 |
+ 7.9 |
5.19 |
13 |
450 ± 51 |
-3.4 |
Females |
|||
0.0 |
16 |
399 ± 61 |
- |
0.37 |
14 |
393 ± 75 |
1.5 |
1.39 |
10 |
368 ± 39 |
-7.8 |
5.19 |
15 |
349 ± 57* |
-12.5 |
÷There were 50 animals m each group at the start of the study.
: At the end of the study.
The value marked with an asterisk differs significantly from the corresponding control value I P < 005t.
Table 3, Summary of neoplasms in rats (F0 that received the test chemical in the diet utero and throughout their lifetimes
Dietary concn of (%) |
Males |
Females |
||||||
0.0 |
0.37 |
1.39 |
5.19 |
0.0 |
0.37 |
1.39 |
5.19 |
|
No. of rats examined |
50 |
37 |
24 |
50 |
50 |
49 |
42 |
50 |
Adrenal |
|
|
|
|
|
|
|
|
Cortical carcinoma |
1 |
0 |
0 |
0 |
0 |
0 |
1 |
2 |
Phaeochromocytma |
1 |
0 |
1 |
3 |
0 |
0 |
0 |
1 |
Brain |
|
|
|
|
|
|
|
|
Glioma |
1 |
0 |
0 |
0 |
2 |
0 |
0 |
0 |
Fibrosarcoma |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Haemolymphoreticular, system |
|
|
|
|
|
|
|
|
Lymphocytic lymphoma |
3 |
4 |
5 |
1 |
1 |
0 |
0 |
1 |
Histiocytic lymphoma |
3 |
1 |
0 |
3 |
4 |
2 |
0 |
2 |
Jejunum |
|
|
|
|
|
|
|
|
Adenocarcinoma |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
Kidney |
|
|
|
|
|
|
|
|
Benign mixed tumour |
1 |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
Transitional cell carcinoma |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Tubular cell carcinoma |
0 |
0 |
1 |
1 |
0 |
0 |
0 |
0 |
Malignant mixed tumours |
1 |
0 |
0 |
0 |
1 |
0 |
0 |
1 |
Hemagiosarcoma |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
Liver |
|
|
|
|
|
|
|
|
Cholangiocarcinoma |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Hepatocellular carcinoma |
2 |
1 |
0 |
0 |
0 |
1 |
0 |
0 |
Neoplastic nodule |
0 |
2 |
0 |
0 |
0 |
0 |
1 |
1 |
Mammary gland |
|
|
|
|
|
|
|
|
Adenocarcinoma |
0 |
1 |
0 |
0 |
5 |
5 |
5 |
3 |
Adenoma |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
Fibroadenoma |
0 |
0 |
0 |
1 |
24 |
28 |
20 |
19 |
Mesenteric lymph node |
|
|
|
|
|
|
|
|
Haemangioma |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Ovary |
|
|
|
|
|
|
|
|
Papillary cystadenoma |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Scirrhous carcinoma |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
Pancreas |
|
|
|
|
|
|
|
|
Adenoma |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
Carcinoma |
1 |
0 |
0 |
2 |
3 |
0 |
0 |
2 |
Skin and subcutaneous tissue |
|
|
|
|
|
|
|
|
Basal cell carcinoma |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Spleen |
|
|
|
|
|
|
|
|
Hemangioma |
1 |
0 |
0 |
1 |
1 |
0 |
0 |
0 |
Hemangiosarcoma |
0 |
1 |
0 |
0 |
0 |
1 |
0 |
0 |
Stomach |
|
|
|
|
|
|
|
|
Squamous cell carcinoma |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
Fibrosarcoma |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
Testis |
|
|
|
|
|
|
|
|
Interstitial cell adenoma |
2 |
0 |
0 |
2 |
0 |
0 |
0 |
0 |
Thymus |
|
|
|
|
|
|
|
|
Carcinoma |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
Thyroid |
|
|
|
|
|
|
|
|
C-cell adenoma |
1 |
1 |
0 |
0 |
0 |
1 |
0 |
3 |
Follicular carcinoma |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
0 |
Uterus |
|
|
|
|
|
|
|
|
Adenocarcinoma |
0 |
0 |
0 |
0 |
1 |
4 |
3 |
1 |
Endometrial polyp |
0 |
0 |
0 |
0 |
0 |
3 |
0 |
2 |
Endometrial sternal sarcoma |
0 |
0 |
0 |
0 |
3 |
1 |
1 |
0 |
Hemangiosarcoma |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Squamous cell carcinoma |
0 |
0 |
0 |
0 |
0 |
0 |
1 |
1 |
Sclerosing adenocarcinoma |
0 |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
Ear |
|
|
|
|
|
|
|
|
Neurofibroma |
0 |
0 |
0 |
0 |
1 |
0 |
0 |
0 |
Eye |
|
|
|
|
|
|
|
|
Neurofibrosarcoma |
0 |
1 |
0 |
0 |
0 |
0 |
0 |
0 |
Applicant's summary and conclusion
- Conclusions:
- The No Observed Adverse Effect level (NOAEL) for the test chemical using male and female Sprague Dawley rats in lifetime study was observed at dose concentration of 2829 and 901 mg/kg bw/day respectively
- Executive summary:
Toxicity of the test chemical was assessed in Sprague Dawley rats in life time study. 30 Sprague Dawley rats per sex per dose group were fed the test chemical in diet at dose concentration of 0, 0.37, 1.39 or 5.19% (0, 180, 701, 2829 mg/kg bw/day for males and 0, 228, 901, 3604 mg/kg bw/day for females), 1 wk before mating, throughout the 3-wk breeding period, and during the gestation and lactation periods. The animals were observed for clinical signs, mortality, morbidity, body weight and food consumption changes, hematology, clinical chemistry, gross and histopathology. No significant compound related adverse effect were observed on mortality, clinical signs, body weight (except for a reduction in body weight in high-dose 3604 mg/Kg bw/day females at the end of the study), food consumption, hematology, clinical chemistry, gross and histopathology. The no observed adverse-effect level (NOAEL) in this study was 5.19% (2829 mg/kg bw/day) for male rats, and 1.39% (901 mg/kg bw/day) for female rats.
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