Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 212-660-9 | CAS number: 839-90-7
- 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
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
- Remarks:
- combined repeated dose and reproduction / developmental screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: according to information in OECD SIDS (2002)
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
- GLP compliance:
- yes
- Limit test:
- no
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: 10 weeks old, both sexes
- Weight at study initiation: 335-364 g for males, 233-263 g for females
IN-LIFE DATES:
- Treatment period, Males: 49 days (14 days before mating and 35 days including 14 days for mating)
Treatment period, Females: 40-46 days (from 14 days prior to mating to day 3 of lactation.)
- Frequency of treatment: Daily
- Post treatment observation period: 1 day
- Duration of test, Males: 50 days
Duration of test, Females: From 14 days prior to mating to day 4 of lactation. - Route of administration:
- oral: gavage
- Vehicle:
- water
- Remarks:
- for injection
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- - Treatment period, Males: 49 days (14 days before mating and 35 days including 14 days for mating)
- Treatment period, Females: 40-46 days (from 14 days prior to mating to day 3 of lactation.) - Frequency of treatment:
- Daily
- Dose / conc.:
- 30 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 100 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 300 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 1 000 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 12
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Post-treatment observation period: 1 day
- Observations and examinations performed and frequency:
- Clinical observations performed and frequency:
- Clinical signs: Twice a day (just before and after administration)
- Body weight, Males: Twice a week
Body weight, Females: Twice a week for pre-mating and mating period, 0, 7, 14, 21st day of pregnancy and 0, 4th day of lactation period.
- Food consumption, Males: Twice a week for pre-mating period and after a mating period end.
Food consumption, Females: Twice a week for pre-mating period, 2, 9, 16, 21st day of pregnancy and 4th day of lactation period.
Hematological examinations (only for males):
Red blood cell count, white blood cell count, platelet count, hemoglobin concentration, hematocrit value, differential leukocyte counts,
protrombin time, activated partial thromboplastin time, fibrinogen, mean corpuscular volume, mean corpuscular hemoglobin,
mean corpuscular hemoglobin concentration, reticulocyte count.
Blood chemical examinations (only for males):
Total protein, albumin, A/G ratio, blood urea nitrogen, creatinine, glucose, total cholesterol, total bilirubin, triglyceride, sodium, potassium,
chloride, calcium, inorganic phosphorus, alkaline phosphatase, AST, ALT, gamma-GTP.
Urinary examinations (only for males): Urinalysis was conducted just before the termination of treatment, and the following items were examined:
Volume, specific gravity, color, pH, protein, glucose, ketone body, bilirubin, occult blood, urobilinogen, urinary sediments.
This study was conducted to examine both repeated dose toxicity and reproductive/developmental toxicity as an OECD screening combined study
(OECD 422 test guideline). Therefore, hematological and blood chemical examinations, and urinalysis for females were not performed. - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes, see below
WEIGHING OF ORGANS: Yes, see below
HISTOPATHOLOGY: Yes, see below
- Terminal sacrifice, Males: Killed on the day after the treatment period.
Terminal sacrifice, Females: Killed on day 4 of lactation. Females with no delivery were killed 4 days after the delivery expected date.
Females with no copulation were killed at the end of the mating period.
- Gross pathology: All rats received a full macroscopic examination with tissue collection.
- Organs Weights: The following organs were weighed at necropsy:
Brain, pituitary, thyroids, heart, thymus, liver, spleen, adrenals, kidneys, testes, epididymides, ovaries.
- Histopathology: The following organs were microscopically observed for the control and 1000 mg/kg bw/day groups:
Brain, pituitary gland, thyroids, heart, thymus, liver, spleen, adrenals, kidneys, testes, epididymides, ovaries,
lung, trachea, pancreas, salivary glands, esophagus, stomach, duodenum, jejunum, ileum, caecum, rectum,
colon, lymph node, bladder, uterus, vagina, parathyroids, spinal cord, sciatic nerve, eyes, Harderian glands,
mammary gland, bone marrow, seminal vesicle, prostate.
In addition, liver and spleen (male only) were also examined for the 30, 100 and 300 mg/kg bw/day groups. - Other examinations:
- Reproductive and developmental toxicity parameters (addressed in separate endpoints).
- Statistics:
- Dunnett's test was used for numerical data.
- 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 specified
- Water consumption and compound intake (if drinking water study):
- not specified
- Ophthalmological findings:
- not examined
- Haematological findings:
- no effects observed
- Description (incidence and severity):
- examined only in males
- Clinical biochemistry findings:
- no effects observed
- Description (incidence and severity):
- examined only in males
- Urinalysis findings:
- no effects observed
- Description (incidence and severity):
- examined only in males
- Behaviour (functional findings):
- not specified
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- only in 2 females, no effect in males
- Histopathological findings: neoplastic:
- not examined
- Details on results:
- Histopathology
Males: No treatment-related abnormality was observed.
Females: Very slight (marginally positive) extramedullary hematopoiesis in the liver was noted in two female animals of the 1000 mg/kg bw/day group. - Key result
- Dose descriptor:
- NOEL
- Effect level:
- >= 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- other: NOEL = highest dose tested. NOEL (instead of NOAEL stated by OECD SIDS) seems more appropriate, because OECD SIDS states: "No treatment related abnormality up to 1000 mg/kg bw/day in parental males."
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 1 000 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- female
- Basis for effect level:
- other: NOAEL = highest dose tested. Very slight extramedullary hematopoiesis in the liver in two parental females at 1000 mg/kg bw/day was statistically not significant, therefore not adverse.
- Key result
- Critical effects observed:
- no
- Conclusions:
- There were no treatment related effects in male rats up to 1000 mg/kg bw/day. The only treatment related effect in females was very slight (marginally positive) extramedullary hematopoiesis in the liver in two female animals of the high dose group (1000 mg/kg bw/day). This finding was considered not to represent an adverse effect, because it did not differ statistically significantly from controls. Therefore, for treated male animals the no observed effect level (NOEL) was estimated to be 1000 mg/kg bw/day and for treated female animals the no observed adverse effect level (NOAEL) was estimated to be 1000 mg/kg bw/day.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Study duration:
- subacute
- Species:
- rat
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
Treatment with THEIC over ca. 45 days did not induce any adverse effects in the OECD 422 study.
Read across of THEIC with cyanuric acid (EC No. 203-618-0, CAS No. 108-80-5) regarding subchronic repeated dose oral toxicity testing was warranted by very similar physico-chemical, ecotoxicological and toxicological properties of both substances and the lack of any adverse effects of THEIC in the available studies. Therefore, the conduct of a subchronic toxicity study with THEIC in the rat would not have provided relevant additional information regarding its toxicological hazard.
For cyanuric acid, sodium salt, WHO/JECFA established a Tolerable Daily Intake level (TDI) of 1.54 mg/kg bw/day. This TDI was based on a broad toxicology data set including a number of reproduction, developmental toxicity and combined chronic toxicity/carcinogenicity studies with cyanuric acid, sodium salt in various species.
Justification for classification or non-classification
In the OECD 422 Study, it was demonstrated that treatment with THEIC at doses up to and including 1000 mg/kg/day for approximately 45 consecutive days did not induce any adverse effects. In addition, THEIC did not induce any adverse effects in any of the other toxicity or ecotoxicity studies. Read-across from study results obtained with cyanuric acid, sodium salt was also favourable and, in view of a TDI of 1.54 mg/kg bw/day, gave no indication of relevant toxicity. Therefore, THEIC does not warrant any classification regarding repeated exposure according to European classification rules [REGULATION (EC) 1272/2008].
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.