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EC number: 233-971-6 | CAS number: 10476-85-4
- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Effects on fertility
Effect on fertility: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 309 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- The study to examine the effects of strontium ranelate on male and female fertility (K. Momburg, 2001) of rats is regarded as relevant and reliable to evaluate the effects of strontium.
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Read across concept:
It is foreseen that read-across from strontium nitrate and strontium ranelate to strontium chloride is possible, since as a first surrogate for bioavailability, the solubility of a test substance may be used. In the gastrointestinal tract (pH ~ 1.5) solubilities at low pH are relvant. All three substances are "soluble” to “very soluble" (6.74 g SrRenelate/L at 37°C/ pH 3.8, 257.5 g SrCl2/L at 37°C/ pH 0.2 and 376.8 g Sr(NO3)2/L at 37°C/ pH 0.3) at low pH. Hence, any read- across from strontium nitrate and strontium ranelate to strontium chloride is considered to be justified.
For more information on solubility testing please refer to the attached file.
Short description of key information:
Male and female fertility was examined in a reproduction toxicity study in male and female Wistar rat with oral administration of dose levels of 500, 750 and 1000 mg/kg bw/d Strontium ranelate. Male and female fertility as well as reproductive performance was not affected at dose level of up to 1000 mg/kg bw/d. Females of the female fertility subgroup were treated for 14 days prior to pairing with untreated males and continued throughout pairing and until day 17 of gestation. Males of the subgroup for male fertility assessment were treated for 28 days prior to pairing with untreated females and continued throughout pairing including the day before sacrifice. Treatment of females of this subgroup started after mating on day six of gestation until day 20 of lactation.
Justification for selection of Effect on fertility via oral route:
Based on data from a reliable GLP reproduction toxicity study with strontium ranelate (Oral reproduction toxicity study in the Wistar rat (male and female fertility/embryo-fetal and postnatal development) adressing male and female fertility according to the ICH guideline on Detection of Toxicity to Reproduction of Medicinal Products, June 24, 1993, and with the ICH Guideline Addendum: Toxicity to male fertility, July 1996.
Effects on developmental toxicity
Description of key information
Strontium ranelate was not teratogenic in rats and rabbits. Only an increase in the frequency of delays in skeletal ossification and structural abnormalities (way ribs, bent bones, shortened and thickened humerus and misshapen clavicle) was observed in the rat at all dose levels. The effects of strontium ranelate on the embryo-fetal and pre-/postnatal development was investigated in a GLP compliant toxicity study according to the ICH guideline on Detection of Toxicity to Reproduction of Medical Products, June 24, 1993. Groups of pregnant female rats were either exposed from day 14 prior to mating with untreated males until day 17 of gestation (group A) or after mating with treated males from day 6 of gestation until day 20 of lactation. Embryo-fetal development was evaluated in group A and effects on parturition and pre-/post natal development in group B. Animals received the test compound by oral gavage at dose levels of 500, 750 and 1000 mg/kg bw/d. Control animals were treated with the vehicle.
No treatment-related maternal toxicity was observed in group A and B females. No effects on embryo/-fetal development were observed beside an increase in the frequency of delays in skeletal ossification and structural abnormalities (way ribs, bent bones, shortened and thickened humerus and misshapen clavicle) at all dose levels. Although the percentage of affected fetuses by a delay of ossification was higher in the treated groups than in the control, there was no dose-response relationship and values were within the normal historical control range of this strain. In addition, the structural abnormalities observed in twenty day old fetuses were completely reversible in seven to eight week old F1 animals, because all these anomalies were no longer visible during postnatal development as shown by X-ray radiography. These transitory findings were regarded as not effecting basical development of offspring but were related to retarded ossification.
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 154 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- The study to examine the effects of strontium ranelate on embryo-fetal and pre-/postnatal development (K. Momburg, 2001) of rats is regarded as relevant and reliable to evaluate the effects of strontium. In addition, a study on the embryo-fetal development of rabbits (K. Momberg 1999) with strontium ranelate is available to complete the database for this endpoint.
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Additional information
The effects of strontium ranelate on the embryo-fetal and pre-/postnatal development was investigated in a GLP compliant toxicity study according to the ICH guideline on Detection of Toxicity to Reproduction of Medical Products, June 24, 1993 (K. Momberg 2001). Groups of pregnant female rats were either exposed from day 14 prior to mating with untreated males until day 17 of gestation (group A) or after mating with treated males from day 6 of gestation until day 20 of lactation (group B). Embryo-fetal development was evaluated in group A and effects on parturition and pre-/post natal development in group B. Animals received the test compound by oral gavage at dose levels of 500, 750 and 1000 mg/kg bw/d. Control animals were treated with the vehicle. Additional subgroups (group C and D) were included for toxicokinetic investigations.
No treatment-related maternal toxicity was observed in group A and B females. No effects on embryo/-fetal development were observed beside an increase in the frequency of delays in skeletal ossification and structural abnormalities (way ribs, bent bones, shortened and thickened humerus and misshapen clavicle) at all dose levels. Although the percentage of affected fetuses by a delay of ossification was higher in the treated groups than in the control, there was no dose-response relationship and values were within the normal historical control range of this strain. In addition, the structural abnormalities observed in twenty day old fetuses were completely reversible in seven to eight week old F1 animals, because all these anomalies were no longer visible during postnatal development as shown by X-ray radiography. These transitory findings were regarded as not effecting basical development of offspring but were related to retarded ossification.
It was also discussed that these findings appear not relevant in the case of human exposure during organogenesis, because the skeletal development at parturition in humans is much more advanced than in rodent species. In conclusion, these findings were not considered as true congenital skeletal malformations, because they were reversible and were therefore considered as variations without any functional consequences.
Although in the context of the study, the lowest dose level of 500 mg/kg bw/d does not represent an NOAEL, but a LOAEL, the findings at this dose level were of transient nature and regarded as not relevant for human embryo/fetal development, and thus did not provide evidence of an adverse effect on the development of offspring.
The structural abnormalities were also not present in theoral embryo-fetal development study with strontium ranelate (K. Momberg 1999) in rabbits at up to 1500 mg/kg bw/d.
In the post-natal development part of the study, a delay of incisor eruption was seen on lactation day 11 mainly in offspring of the 1000 mg/kg bw/d group, but had no negative effect on animal growth which is directly related to feed intake and use of teeth for gnawing of feed pellets. In addition, the relevance of these effects for humans was deemed as low, because tooth development in man differ from rat with incisor eruption occurring after weaning at 6-24 months after birth. Therefore, the NOAEL for postnatal development was established at the highest dose group of 1000 mg/kg bw/d.
In addition, in the study published by Lansdownet al. (1972) (see 7.8.2 "s_Lansdown_1972) groups of 3 female Wistar rats were treated subcutaneously with 25, 50, 100 or 200 mg strontium nitrate/kg bw/d in 1 ml distilled water from day 9 to 19 of pregnancy when they were killed. Control animals received distilled water only. The progeny from strontium-treated mothers did not differ from that of controls in size or body weight. The litter sizes were normal and the number of resorption sites was not increased. No histological changes were detected in the soft tissues and the skeletal tissues exhibited the characteristic degree of ossification for 19-day old rat foetuses. The results indicated that high doses of strontium nitrate (up to and including 200 mg/kg bw/d s.c.) are not teratogenic. Thus, the dose of 200 mg/kg bw/d can be considered as a NOAEL for developmental toxicity which corresponds to an external dose of about 83 mg Sr/kg bw/d (equal to 150 mg SrCl2/kg bw/d) to female rats. However, the study was conducted only in a small number of females (p=3) per group and only a limited number of parameters were evaluated. In addition, the subcutaneous route of administration is not relevant route of exposure for risk assessment purposes. Nevertheless, the study by Lansdownet al. (1972) on pregnant rats is regarded as an appropriate study to support the evaluation of the effects of stronium on embryo-fetal development.
Justification for selection of Effect on developmental toxicity: via oral route:
Data from a reliable GLP reproduction toxicity study with strontium ranelate (Oral reproduction toxicity study in the Wistar rat (male and female fertility/embryo-fetal and postnatal development) addressing embryo-fetal and pre-/postnatal development of offspring according to the ICH guideline on Detection of Toxicity to Reproduction of Medicinal Products, June 24, 1993, and with the ICH Guideline Addendum: Toxicity to male fertility, July 1996.
Justification for classification or non-classification
Based on the overall evaluation of the available data for strontium on reproduction and developmental toxicity, no classification and labelling for reproduction is deemed to be justifiedaccording to regulation (EC) 1272/2008.
Additional information
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