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EC number: 252-652-2 | CAS number: 35642-64-9
- 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
NOAEL was estimated to be 779 mg/kg bw when Wistar male and female rats were orally exposed with 7-[[2-[(aminocarbonyl)amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid.
Thus, as per criteria of CLP regulation, 7-[[2-[(aminocarbonyl) amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid can be not classified for reproductive toxicity.
Link to relevant study records
- Endpoint:
- toxicity to reproduction
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with limited documentation / justification
- Justification for type of information:
- Prediction is done using OECD QSAR toolbox version 3.4 and the supporting QMRF report has been attached.
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- Prediction is done using OECD QSAR Toolbox version 3.4 with respect to the descriptor log Kow.
- GLP compliance:
- not specified
- Limit test:
- no
- Specific details on test material used for the study:
- Name of the test chemical: 7-[[2-[(aminocarbonyl)amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid
Molecular formula: C20H16ClN9O10S3
Molecular weight: 674.0504 g/mol
Smiles Notation: S(=O)(=O)(c1c(/N=N/c2c(NC(=O)N)cc(Nc3nc(nc(n3)Cl)N)cc2)cc2c(S(=O)(=O)O)cc(S(=O)(=O)O)cc2c1)O
InChI: 1S/C20H16ClN9O10S3/c21-17-26-18(22)28-20(27-17)24-9-1-2-12(13(5-9)25-19(23)31)29-30-14-7-11-8(4-16(14)43(38,39)40) 3-10(41(32,33)34)6-15(11)42(35,36)37/h1-7H,(H3,23,25,31)(H,32,33,34)(H,35,36,37)(H,38,39,40)(H3,22,24,26,27,28)/b30-29+
Substance Type: Organic
Physical State: solid - Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Route of administration:
- oral: gavage
- Type of inhalation exposure (if applicable):
- not specified
- Vehicle:
- not specified
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- Premating exposure period: 2 weeks for male rats
2 weeks for female rats
Exposure period: 22 days
Duration of the test: approx. 54 days - Frequency of treatment:
- Daily
- Details on study schedule:
- not specified
- Dose / conc.:
- 779 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- not specified
- Control animals:
- not specified
- Details on study design:
- not specified
- Positive control:
- not specified
- Parental animals: Observations and examinations:
- not specified
- Oestrous cyclicity (parental animals):
- not specified
- Sperm parameters (parental animals):
- not specified
- Litter observations:
- not specified
- Postmortem examinations (parental animals):
- not specified
- Postmortem examinations (offspring):
- not specified
- Statistics:
- not specified
- Reproductive indices:
- not specified
- Offspring viability indices:
- not specified
- Clinical signs:
- no effects observed
- Dermal irritation (if dermal study):
- not specified
- Mortality:
- not specified
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Immunological findings:
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- not specified
- Other effects:
- not specified
- Reproductive function: oestrous cycle:
- not specified
- Reproductive function: sperm measures:
- not specified
- Reproductive performance:
- not specified
- Dose descriptor:
- NOAEL
- Effect level:
- 778.77 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- clinical signs
- body weight and weight gain
- food consumption and compound intake
- gross pathology
- histopathology: non-neoplastic
- Remarks on result:
- other: No effects observed.
- Critical effects observed:
- not specified
- System:
- other: not specified
- Organ:
- not specified
- Treatment related:
- not specified
- Dose response relationship:
- not specified
- Relevant for humans:
- not specified
- Remarks on result:
- not measured/tested
- Clinical signs:
- not specified
- Dermal irritation (if dermal study):
- not specified
- Mortality / viability:
- not specified
- Body weight and weight changes:
- not specified
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not specified
- Haematological findings:
- not specified
- Clinical biochemistry findings:
- not specified
- Urinalysis findings:
- not specified
- Sexual maturation:
- not specified
- Organ weight findings including organ / body weight ratios:
- not specified
- Gross pathological findings:
- not specified
- Histopathological findings:
- not specified
- Other effects:
- not specified
- Behaviour (functional findings):
- not specified
- Developmental immunotoxicity:
- not specified
- Dose descriptor:
- other: not specified
- Generation:
- other: not specified
- Based on:
- not specified
- Sex:
- not specified
- Basis for effect level:
- other: not specified
- Remarks on result:
- other: not specified
- Critical effects observed:
- not specified
- System:
- other: not specified
- Organ:
- not specified
- Treatment related:
- not specified
- Dose response relationship:
- not specified
- Relevant for humans:
- not specified
- Remarks on result:
- not measured/tested
- Reproductive effects observed:
- not specified
- Treatment related:
- not specified
- Relation to other toxic effects:
- not specified
- Dose response relationship:
- not specified
- Relevant for humans:
- not specified
- Conclusions:
- The NOAEL was estimated to be 779 mg/kg bw when Wistar male and female rats were orally exposed with 7-[[2-[(aminocarbonyl)amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid.
- Executive summary:
In a prediction done by SSS (2017) using the OECD QSAR toolbox with log kow as the primary descriptor, the reproductive toxicity was estimated for 7-[[2-[(aminocarbonyl)amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid. The NOAEL was estimated to be 779 mg/kg bw when Wistar male and female rats were orally exposed with 7-[[2-[(aminocarbonyl)amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid.
Reference
The
prediction was based on dataset comprised from the following
descriptors: NOAEL
Estimation method: Takes average value from the 6 nearest neighbours
Domain logical expression:Result: In Domain
((((("a"
or "b" )
and ("c"
and (
not "d")
)
)
and "e" )
and "f" )
and ("g"
and "h" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Acid moiety OR Anilines
(Unhindered) OR Substituted Ureas OR Triazines, Aromatic by Aquatic
toxicity classification by ECOSAR ONLY
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as Activated N-heterocycles by Skin
irritation/corrosion Inclusion rules by BfR
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as Group 14 - Carbon C AND Group 15
- Nitrogen N AND Group 16 - Oxygen O AND Group 16 - Sulfur S AND Group
17 - Halogens Cl AND Group 17 - Halogens F,Cl,Br,I,At by Chemical
elements
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as Group 17 - Halogens F by
Chemical elements
Domain
logical expression index: "e"
Similarity
boundary:Target:
NC(=O)Nc1cc(Nc2nc(N)nc(Cl)n2)ccc1N=Nc1cc2c(cc1S(O)(=O)=O)cc(S(O)(=O)=O)cc2S(O)(=O)=O
Threshold=10%,
Dice(Atom centered fragments)
Atom type; Count H attached; Hybridization
Domain
logical expression index: "f"
Similarity
boundary:Target:
NC(=O)Nc1cc(Nc2nc(N)nc(Cl)n2)ccc1N=Nc1cc2c(cc1S(O)(=O)=O)cc(S(O)(=O)=O)cc2S(O)(=O)=O
Threshold=20%,
Dice(Atom centered fragments)
Atom type; Count H attached; Hybridization
Domain
logical expression index: "g"
Parametric
boundary:The
target chemical should have a value of log Kow which is >= -2.09
Domain
logical expression index: "h"
Parametric
boundary:The
target chemical should have a value of log Kow which is <= 3.24
Effect on fertility: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 779 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- The data is Klimicsh 2 and from OECD QSAR toolbox version 3.3 (2017).
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Reproductive toxicity:
In different studies, 7-[[2-[(aminocarbonyl)amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid has been investigated for reproductive toxicity to a greater or lesser extent. Often are the studies based on in vivo experiments and estimation in rodents, i.e. most commonly in rats for 7-[[2-[(aminocarbonyl)amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid along with the study available on structurally similar read across substance FD & C RED NO. 40 (CAS no 25956-17-6), RED 2G (CAS no 3734-67-6) and FD &C Red 4 (CAS No.- 4548-53-2) The predicted data using the OECD QSAR toolbox has also been compared with the experimental studies.
In a prediction done by SSS (2017) using the OECD QSAR toolbox with log kow as the primary descriptor, the reproductive toxicity was estimated for 7-[[2-[(aminocarbonyl) amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid. The NOAEL was estimated to be 779 mg/kg bw when Wistar male and female rats were orally exposed with 7-[[2-[(aminocarbonyl)amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid.
In another experimental study Collins et al (Food Chem. Toxic. Vol. 27, No. 11, pp. 707-713. 1989) on structurally similar read across substance FD & C RED NO. 40 (CAS no 25956-17-6), Osborne-Mendel female rat were treated with FD & C RED NO. 40 in the concentration of 0, 30, 75, 150, 300, 600 and 1000 mg/ kg bw orally by gavage from Gestation day 0 to day 19. Initial body weight at day 0 and maternal body-weight gain during gestation were similar in all groups. Mean food consumption on days 0-7, 7-14, 14-20 and 0-20 of treated animals was similar to that of the control animals. Similarly, No unusual behaviors were observed in the animals during the study. The pregnancy rate ranged from 85.71 to 95.35% with no evidence of dose correlation. The mean numbers of corpora lutea and implants per female were similar in all groups. No litters were totally resorbed were observed as compared to control. In addition, the mean number of viable foetuses per female was similar in all groups. The number of early deaths per litter and the number of early plus late deaths per litter were greatest in the 600 mg/kg group, but these appeared to be random occurrences. The percentage of females with at least one resorption was similar in all groups. The percentage of females given 600 mg/kg that had at least two resorptions was significantly greater than the percentage in the control females, but there was no dose related effect in the percentage of females with at least two resorptions. Mean foetal weights of males and females and crown rump lengths were similar in all groups. The number of litters with runts was similar in all groups. No dose-related changes were seen in foetal viability, body weight, body length, sex distribution or external variations. Skeletal and soft-tissue development appeared similar in foetuses of all groups. The isolated increases that occurred in the number of male foetuses, number of females with two or more resorptions, number of litters with three or more sternebral variations and incidence of 14thrib bud are considered random occurrences and were not related to dosage. Therefore, NOAEL was considered to be 1000 mg/kg bw for P and F1 generation when Osborne-Mendel female rat were treated with FD & C RED NO. 40 orally by gavage from gestation day 0 to day 19.
Further supported by experimental study given by NTRL (NTRL, OTS0516606-2, 1989) on structurally similar read across substance RED 2G (CAS no 3734-67-6), male and female mice were treated with RED 2G in the concentration of 0, 30, 150,750 and 1500 mg/kg bw/day in feed. No effect on survival, body weight and food consumption of treated mice were observed as compared to control. Increased heinz bodiez and methaemoglobins and decreased packed cell volumes were observed at 750 and 1500 mg/kg bw/day as compared to control. Similarly, Increase in relative spleen weight and splenic size were observed at 750 and 1500 mg/kg bw/day treated mice as compared to control. In addition, increased erythropoiesisand increased haemosiderin content, increase in haemosiderin in tile pruximal convoluted tubules of the kidney and Erytbroid hyperplasia of bone marrow were observed at 750 and 1500 mg/kg bw/day, Lesions in the liver were observed at 1500 mg/kg bw/day and Haemosiderin in the spleens were observed at 150 mg/kg bw/day treated mice as compared to control. No effect on histopathology of testes, uterus and ovaries were observed in treated mice. Therefore, NOAEL was considered to be 1500 mg/kg bw/day for F0 generation when male and female mice were treated with RED 2G orally in diet for6 weeks.
Again supported by experimental study conducted by Carsonet al(J. Toxicol.-Cut. & Ocular Toxicol. 3(3), 309-331 (1984)) on structurally similar read across substance FD&C Red 4 (CAS No 4548-53-2), Swiss-Webster male and female mice were treated with FD &C Red 4 (CAS No.- 4548-53-2) in the concentration of 1500 mg/kg bw/day in distilled water applied twice weekly on 6 cm2 dorsal area of skin. No effects were observed on survival, clinical sign and body weight of treated male and female mice as compared to control. Similarly, lesion in Mammary Gland and Subcutaneous papillary were obseved gross pathologically in treated mice, but the observed effects were similar to control. In addition, All grades malignant lymphoma and variation in nuclear morphology in liver, infarction, malignant and myeloid metaplasia, leukocytic aggregations in spleen, all grades malignant lymphoma, leukemic and round cell infiltration and leukocytic aggregation in kidneys, malignant lymphoma in lymph nodes, malignant lymphoma, Inflammation, pneumonitis, bronchitis and necrotic changes in lungs and all grades malignant lymphoma in thymus were observed in male and female treated mice. No significant difference in the incidence of this lesion were observed as compared to control and considered to be not treatment related. Therefore, NOAEL was considered to be 1500 mg/kg bw/day when Swiss-Webster male and female mice were treated with FD&C Red 4.
Thus, based on the above study and predictions on 7-[[2-[(aminocarbonyl)amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid and its read across substances, it can be concluded that NOAEL value is 779 mg/kg bw with no effect on reproduction. Thus, as per criteria of CLP regulation, 7-[[2-[(aminocarbonyl) amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid can be not classified for reproductive toxicity.
Effects on developmental toxicity
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
Based on the above study and predictions on 7-[[2-[(aminocarbonyl)amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid and its read across substances, it can be concluded that NOAEL value is 779 mg/kg bw with no effect on reproduction. Thus, as per criteria of CLP regulation, 7-[[2-[(aminocarbonyl) amino]-4-[(4-amino-6-chloro-1,3,5-triazin-2-yl)amino]phenyl]azo]naphthalene-1,3,6-trisulphonic acid can be not classified for reproductive toxicity.
Additional information
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