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EC number: 204-289-6 | CAS number: 118-96-7
- 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

Carcinogenicity
Administrative data
Description of key information
Justification for selection of carcinogenicity via oral route
endpoint:
One publication available.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Link to relevant study records
- Endpoint:
- carcinogenicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 453 (Combined Chronic Toxicity / Carcinogenicity Studies)
- GLP compliance:
- yes
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Route of administration:
- oral: feed
- Duration of treatment / exposure:
- 24 months
- Frequency of treatment:
- Test animals received weekly doses, based on their body weight and food consumption.
- Dose / conc.:
- 0 mg/kg bw/day (nominal)
- Dose / conc.:
- 0.4 mg/kg bw/day (nominal)
- Dose / conc.:
- 2 mg/kg bw/day (nominal)
- Dose / conc.:
- 10 mg/kg bw/day (nominal)
- Dose / conc.:
- 50 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 75 rats per sex
- Control animals:
- yes
- Details on study design:
- The doses were selected based on the results of 13-week oral (diet) toxicity studies in Fischer 344 rats.
- Sacrifice and pathology:
- Ten rats per sex per dosegroup were sacrificed following six and 12 months, with surviving animals sacrificed at the end of the 24-month treatment.
- Details on results:
- Survival rates and mean survival duration did not differ among control and treated groups in either sex. Dose-related reductions in body weight (5- 14% reduction in animals given 10 mg TNT/kg/day, and 30-33% decreases in the 50 mg/kg/day groups) and food intake were observed in both males and females. There was a dose-related increase in the incidence of hepatocellular hyperplasia in male rats (23/54, p<0.01;34/55,p<0.01) in the10 mg/kg/day and 50 mg/kg/day dose groups, respectively.Hyperplasia was elevated in the kidney(10 mg/kg/day: 7/47,p<0.05) and urinary bladder (10 mg/kg/day: 12/47,p<0.01) in female rats at doses of 10 mg/kg/day or greater.The incidences of benign and malignant urinary bladder tumors were significantly increased in treated female rats in the 50 mg/kg/day dose group, with an incidence of urinary bladder papilloma and carcinoma (combined) of 17/55 (p<0.01) as compared to 0/54 in controls.
- Key result
- Dose descriptor:
- LOAEL
- Effect level:
- 10 mg/kg bw/day (nominal)
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- clinical biochemistry
- clinical signs
- food consumption and compound intake
- haematology
- ophthalmological examination
- organ weights and organ / body weight ratios
- other: gross and tissue morphology.
- Remarks on result:
- other: Effect type: carcinogenicity
Reference
The observance of carcinoma of the urinary bladder suggests that TNT is a carcinogen to F344 rats under the conditions of the present study. Hepatocellular, renal and urinary bladder hyperplasia supports this concept. These hyperplastic/neoplastic lesions were seen at dosed of 10 mg/kg/day or greater. Additional toxic effects of TNT seen primarly at 50 mg/kg/day included increased numbers of circulating platelets, elevated blood calcium, and increased hearth weights. Tissues morphology studies did not support these observations.
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LOAEL
- 10 mg/kg bw/day
- Study duration:
- chronic
- Species:
- rat
- Quality of whole database:
- Klimisch rating 1.
Carcinogenicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
The observance of carcinoma of the urinary bladder suggests that TNT is a carcinogen to F344 rats under the conditions of the present study. Hepatocellular, renal and urinary bladder hyperplasia supports this concept. These hyperplastic/neoplastic lesions were seen at dosed of 10 mg/kg/day or greater. Additional toxic effects of TNT seen primarly at 50 mg/kg/day included increased numbers of circulating platelets, elevated blood calcium, and increased hearth weights. Tissues morphology studies did not support these observations.
Based on available data, the pure TNT (concentration of impurities 2,4 -DNT; 2,6 -DNT and 3,4 -DNT in amount of total <0.1) does not meet the criteria for classification as carcinogenic
As far as TNT can contain 2,4 -DNT; 2,6 -DNT and 3,4 -DNT in amount of total >0.1 which are all classified as carcinogenic category 1B according to Regulation EC no 1272/2008, we can expect that TNT with those impurities is carcinogenic (calculation method).
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