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EC number: 242-367-1 | CAS number: 18480-07-4
- 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
Supporting data on Strontium ranelate, Strontium chloride and Strontium nitrate show that strontium is not expected to have a mutagen or a carcinogen potential.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
Justification for classification or non-classification
An indirect effect of strontium through activation of thyrocalcitonin production was regarded as unlikely by the authors of the study, since no parafollicular cell hyperplasia was noticed and no effects on CA serum levels were found. In addition, the effects of Sr on thyroid function was discussed in the context of a scientific discussion paper of the EMEA on strontium ranelate, because in the carcinogenicity study in rats an increased incidence of C-cell carcinoma in thyroids of male rats was seen, but this effect was not clearly dose-related and was found to be within the control range in other studies with the strain of rats used. Furthermore, no increased incidence of C-cell hyperplasia or adenoma was seen in the carcinogenicity study rats, and it is also mentioned in the discussion paper that no increase in thyroid C-cell proliferative lesions or in circulating calcitonin levels were found in a 52-week toxicity study in rats. Therefore, it can be concluded that based on the available animal data strontium does not have the potential to produce significant toxicity, or to be harmful to humans, following repeated exposure at low or moderate exposure concentrations relevant for classification.
Additional information
According to the EMEA report 2005, the results of a 105 weeks carcinogenicity in male and female rats, indicate some increased incidences of C-cell carcinoma in thyroids of male rats in the low (LD) and high dose (HD) groups. It is stated that it cannot completely be excluded that a subtle increase in plasma cation levels may have, in some individual rats, affected the progress on of thyroid C-cell hyperplasia/adenoma to carcinoma. However, taking the totality of the data into account, there is no clear evidence that the finding of increased incidences of C-cell carcinoma in LD and HD males in the main carcinogenicity study in the rat are related to strontium ranelate treatment. Moreover, there are some differences between human and rat with respect to calcitonin regulation, such as the age-related increased increase in calcitonin in rats, whereas the opposite occurs with increasing age in humans, which indicate that the tumour findings are of minor clinical relevance. In addition, the incidence of C-cell tumours was not increased in female rats and in male and female mice, and male F344 rats treated over 52 weeks with doses as in the carcinogenicity studies had no increase in thyroid C-cell proliferative lesions.
There is an absence of any published evidence on the formation of tumours in humans after exposure to stable strontium compounds. Information is available on the action of strontium in in-vivo and in-vitro screening systems for the prediction of mutagenicity or carcinogenicity of metal salts. The DNA synthesis in nuclear epithelia of kidney and liver was not inhibited by intra-peritoneal injection of strontium nitrate to mice (Amlacher, 1983). Investigations in an in-vitro screening system showed that strontium chloride did not affect the accuracy of the DNA synthesis (Sirover, 1976).
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