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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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
Description of key information
Reliable acute toxicity data for invertebrates are available for sulfide, sulfate and barium. Barium and sulfide are released upon dissolution of BaS in the aqueous environment. Sulfide is rapidly oxidised under natural environmental conditions. Thus, only acute but not long-term effects due to sulfide exposure are expected. Further, the acute toxicity of sulfate was considered. However, sulfate is of low toxicity.
A reliable 96h-LC50of 0.020 mg H2S/L for the larvae of the mayfly Beatis vagans has been reported by Oseid and Smith (1974) corresponding to the 96h-LC50of 99.4 µg BaS/L.
For the marine environment, the lowest reliable acute value was 0.032 mg H2S/L for the penaid prawn Penaeus indicus (Gopakumar and Kuttyamma, 1996) corresponding to the 96h-LC50of 0.159 mg BaS/L.
A reliable, nominal 48h-EC50of 14.5 mg Ba/L forDaphnia magnais reported by Biesinger and Christensen (1972) resulting ´by read-across ín the 48h-EC50of 17.9 mg BaS/L.
Comparing acute toxicity levels of Ba and S in freshwater, it can be concluded that the acute toxicity of BaS to invertebrates is driven by sulfide resulting in the 96h-LC50 of 0.099 mg BaS/L.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 99.4 µg/L
Marine water invertebrates
Marine water invertebrates
- Effect concentration:
- 159 µg/L
Additional information
Biesinger and Christensen (1972) reported a nominal 48h-EC50of 14.5 mg Ba/L for the water fleaDaphnia magna(total Ba concentrations).
The lowest reliable acute toxicity endpoint for freshwater invertebrates with regard to sulfide was reported by Oseid and Smith (1974) for the larvae of the mayflyBeatis vagans, i.e., the 96h-LC50of 0.02 mg H2S/L corresponding to 0.099 mg BaS/L. Gopakumar and Kuttyamma (1996) reported the lowest reliable acute toxicity endpoint in the marine environment for the penaeid prawnPenaeus indicus, i.e., the96h-LC50of 0.032 mg H2S/L corresponding to 0.159 mg BaS/L.
In oxic environments, however, sulfide released from BaS is oxidized to sulfate, and the hazard of the released sulfur should be evaluated by reading-across the toxicity of sulfate. The study by Mount et al (1997) was identified in the OECD SIDS for Na2SO4(i.e., the most relevant substance for assessing the hazard of sulfate) as key study with regard to acute toxicity of sulfate to invertebrates. This study reports a 48h-LC50of 3080 mg Na2SO4/L for the water fleaCeriodaphnia dubiacorrespondingtoa 48h-LC50of 3673 mg BaS/L.
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