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EC number: 237-159-2 | CAS number: 13674-87-8
- 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
The results obtained in a two year carcinogenicity study (Stauffer Chemical Company, 1981a; Freudenthal, R.I. and Henrich, R.T., 2000) indicate possible concern for man due to the development of adenomas (renal, hepatocellular and adrenal) in addition to Leydig cell tumours in rats.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Endpoint conclusion
- Dose descriptor:
- LOAEL
- 5 mg/kg bw/day
Justification for classification or non-classification
TDCP is classified as Carc. Cat. 2 H351 " suspected causing cancer” based on the results of the above carcinogenicity study further supported by a non-genotoxic mode of action for carcinogenic effects for TDCP.
Additional information
In a 2-year carcinogenicity study, in which groups of 60 male and 60 females rats were fed diets containing TDCP to achieve dose levels of 0, 5, 20 and 80 mg/kg/day, there was a significant increase in the incidence of renal cortical adenomas in mid and high dose animals at 24 months. There was no increase at 12 months. The incidence of benign testicular interstitial cell tumours was also increased in the mid- and high-dose animals at both 12 and 24 months. Hepatocellular adenomas and adrenal cortical adenomas were statistically increased in the high dose animals at 24 months.
In the testes, there was an increased incidence of Leydig cell tumours in the mid and high dose males at both 12 and 24 months. The mechanism by which TDCP induces such tumours is not known. It is reported that one non-genotoxic mode of action by which chemicals can induce such tumours is attributed to alterations in the Hypothalmus-Pituitary-Testis (HPT) Axis which results in elevated levels of luteinising hormone (LH). Increases in LH levels have been shown to be necessary for the induction of Leydig cell tumours through chronic stimulation of the Leydig cells. There are seven known non-genotoxic hormonal mechanisms which have the potential to disrupt the HPT axis leading to Leydig cell tumour induction. Two of these modes of action are not considered of relevance to humans (GnRH antagonism and dopamine agonism) (Clegg et al.,1997). However, the other five mechanisms, (5 α-reductase inhibition, androgen receptor antagonism, inhibition of testosterone biosynthesis, aromatase inhibition and exogenous oestrogen agonism) have been considered to be potentially relevant to humans.
Overall, while the mode of action by which these tumours are induced cannot be identified, there may be some concern for man regarding their formation.
A LOAEL of 5 mg/kg/day is based on the hyperplasia of the convoluted tubule epithelium with increased incidences observed in all treated male animals and in high dose females at 24 months. Hyperplasia was observed from the lowest dose tested. Hyperplasia is often considered as a pre-neoplastic lesion, which can lead to tumour formation. The study report does not provide enough detailed information to conclude whether the hyperplasia observed following treatment with TDCP would progress to cancer or whether the tumours observed with TDCP arise through a different mechanism. However, it is not unreasonable to assume that the tumours have developed through hyperplastic changes.
There is some evidence to suggest that TDCP is mutagenic in vitro. However, in vivo mutagenicity studies were negative, indicating that, in vivo, TDCP is non-genotoxic. This indicates that TDCP may be assumed to be a threshold carcinogen.
In a study carried out to look at the mortality experience of worker in a TDCP manufacturing plant, there was a higher than expected number of lung cancers among male workers. However, the report concluded that there was no evidence linking these lung cancers with exposure to TDCP. There were no other cancers observed.
Carcinogenicity: via oral route (target organ): urogenital: kidneys; urogenital: testes
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