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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
Endpoint summary
Administrative data
Description of key information
- 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 microorganisms
No or few ecotoxicological data are available for strontium hydroxide itself. However, an analogue approach is used for the read-across of ecotoxicological properties of strontium hydroxide from strontium chloride or strontium nitrate, based on the hypothesis that properties are likely to be similar as a result of the presence of a common metal ion Sr2+. Further information on the read-across justification is included as attachment in Section 13.
The analogue approach was applied to the following endpoints:
Additional information
Short-term toxicity data
Reliable acute data are available for three trophic levels: algae, invertebrates and fish.
· An unbounded value of >43.3 mg Sr/L was identified for algae.
· The only bounded acute value of 125 mg Sr/L is available for the invertebrate D. magna.
· The lowest acute effect value (based on measured Sr in the test medium) was an unbounded value of >40.3 mg Sr/L for the fish C. carpio.
It should be noted that the actual E(L)C50values for fish and algae may be well above the reported values as not even partial effects (i.e., mortality or growth rate inhibition) were noted at the highest test concentrations.The table below provides an overview of the most sensitive, reliable, short-term toxicity freshwater data available for strontium.
Table: Most sensitive reliable short-term toxicity endpoints for strontium in freshwater
Species | Parameter | Endpoint | Value (mg Sr/L) | Reference |
Acute fish data |
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Cyprinus carpio | mortality | 96h-LC50 | > 40.3 | Tobor-Kaplon (2010) |
Acute invertebrate data |
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Daphnia magna | mortality/immobility | 48h-LC50 | 125 | Biesinger and Christensen (1972) |
Algal data |
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Pseudokirchneriella subcapitata | growth rate | 72h-ErC50 | > 43.3 | Tobor-Kaplon (2010) |
Long-term toxicity data
Reliable studies on chronic toxicity of strontium to the aquatic environment are available for three trophic levels: algae, invertebrates and fish. The toxicity tests were performed using strontium nitrate or strontium chloride hexahydrate as test substance.
· In the study of growth inhibition of the algal species Pseudokirchneriella subcapitataby strontium nitrate to,all significant effect levels (acute and chronic) were equal or higher than 43.3 mg Sr/L (conservative value). Thus, the 72-h NOEC is ≥ 43.3 mg Sr/L.
· The study on the chronic toxicity of strontium to invertebrates (Biesinger and Christensen, 1972) reported a calculated NOEC for Daphnia magna (i.e., EC16/2) of 21 mg Sr/L.
· A chronic fish study according to OECD 210 (Egeler and Morlock, 2013) was performed with Danio rerio. The NOEC (nominal) was set to ≥100 mg/L for strontium nitrate, corresponding to a re-calculated NOEC (nominal) for strontium of ≥ 41.4 mg/L.
The PNECaquatic calculation will be conducted using the assessment factors method since a large dataset from long-term tests for different taxonomic groups is not available, a Species Sensitivity Distribution (SSD) cannot be developed and statistical extrapolation methods can thus not be used to derive the PNECaquatic. An overview of available long-term data used for PNEC-derivation is provided in the Table below.
Table: Most sensitive reliable long-term toxicity data for strontium in freshwater
Species | Parameter | Endpoint | Value | Reference |
Danio rerio | mortality | 34d-NOEC | ≥ 41.4 | Egeler and Morlock (2013) |
Pseudokirchneriella subcapitata |
| 72-h NOECr | ≥ 43.3 | Tobor-Kaplon (2010) |
Daphnia magna | mortality | 21d-NOEC | 21 | Biesinger and Christensen (1972) |
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