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EC number: 244-214-4 | CAS number: 21109-95-5
- 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
Long-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
The release of barium upon dissolution of BaS determines the chronic toxicity of BaS to fish under normal environmental conditions, and the unbounded NOEC of ≥ 1.55 mg BaS/L (dissolved) is considered in the CSA.
Toxicity data for sulfate were not identified; it should be noted that sulfide will rapidly oxidize to the less toxic sulfate under normal environmental conditions that are relevant for the aquatic environment. Sharma and Yuan (2010), for example, demonstrated that sulfide is oxidised to sulfate and other oxidised S-forms in less than one hour.
Key value for chemical safety assessment
Additional information
Reliable chronic toxicity data for fish are available for barium and sulfide but not for sulfate.
The lowest reliable chronic toxicity for fish with regard to sulfide was reported by Smith et al (1976a) for mortality of the juvenile bluegillLepomis macrochirus, yielding in an unbounded 826d-NOEC of 0.0046 mg H2S/L. Toxic effects of released sulfide from BaS are not relevant for the chronic hazard assessment of BaS as it is oxidized to sulfate, and thus the toxicity of sulfate should be assessed. In freshwater, however, sulfate appears to be of low toxicity to fish with acute LC/EC50 values far above 1000 mg/L. The solubility product constant of barium sulfate of 1.1×10–10 indicates that once sulfide released from BaS is oxidized to sulfate, and that barite (BaSO4) precipitates. Further, sulfate is essential to all living organisms, their intracellular and extracellular concentrations are actively regulated and thus, sulfates are of low toxicity to the environment (OECD SIDS for Na2SO4). Therefore, it may conservatively be assumed that the toxicological moiety of concern for the long-term toxicity of BaS to fish (if any) is barium and further that the contribution of sulfate to the overall toxicity of BaS may be neglected.
One reliable long-term toxicity study (Klimisch 1, GLP) withDanio reriowas conducted. No effects were abserved at the highest test concentration of nominal 100 mg barium dichloride dihydrate/L corresponding to the following unbounded NOEC values:
a) The NOEC ≥ 49.7 mg BaS/L (≥ 40.3 mg Ba/L) based on total barium concentration.
(b) The NOEC ≥ 1.55 mg BaS/L (≥ 1.26 mg Ba/L) based on dissolved barium concentration.
Sulfate released from 1.55 mg BaS/L remains below typical baseline levels for sulfate in pristine surface waters. The median value for sulfate in the FOREGS dataset amounts to 16.1 mg/L (www.gtk.fi/publ/foregsatlas). Thus, the contribution of sulfate to the overall toxicity of BaS may be neglected.Based on findings for other taxonomic groups and exposure periods, it is concluded that the chronic toxicity of BaS under normal environmental conditions is determined by the release of barium and the unbounded NOEC of ≥ 1.55 mg BaS/L (dissolved) is considered in the CSA.
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